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Abstract and Figures

The present survey was undertaken to provide the first census of the marine flora (macroalgae and seagrasses) of Baa Atoll, one of the 26 Maldivian atolls, and to serve along with the macro-fauna biodiversity inventories for conservation purposes. Species collection and inventories have been conducted at 27 sites covering the widest selection of habitats recognized based on satellite images including islands shorelines, reef flats, faros, patch reefs, passes as well as shallow and deep outer reef slopes. A total of 405 specimens were collected and 176 species representing 10 Phaeophyceae, 58 Chlorophyta, 108 Rhodophyta and two seagrasses were identified. The lagoon patch reefs and the oceanic reef slopes were the most diverse geomorphological habitat types and displayed the highest species richness with 38 spp. All lagoon sites shown a similar richness compared to each other with an average species number of 26 spp, while the deep lagoon floor and the seagrass beds in oceanic-exposed reef flats were the less species-rich habitats. The most common species, occurring at all visited sites, were Tydemania expeditionis and Halimeda minima and the most species rich genera appeared to be Halimeda and Caulerpa. No community structure nor strongly supported species assemblages associated to geomorphological habitat types was found. Previous lists available for other Maldivian atolls listed 208 algal species. Sixty of these records were found in Baa Atoll while 113 of the species recorded in the present study represent new records for the Maldives bringing the total number of algal species to 321. The resulting species list shows that the Maldivian algal flora is typically tropical and most of the species belong to the Indo-Pacific biogeographic province. In this paper, we give a general description of the representative macrophyte communities of Baa Atoll in relation to the geomorphology of reefs.
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ATOLL RESEARCH BULLETIN NO. 590
Issued by
NATIONAL MUSEUM OF NATURAL HISTORY
SMITHSONIAN INSTITUTION
WASHINGTON, D.C. U.S.A.
JANUARY 2012
Edited by
Serge Andréfouët
BIODIVERSITY, RESOURCES, AND CONSERVATION
OF
BAA ATOLL (REPUBLIC OF MALDIVES):
A UNESCO MAN AND BIOSPHERE RESERVE
________________________________________________________
1!"#$%$&$'()'*)+,)-+,)'./&-'0)'123)0/..)4)"$5'67895':/&42;5':)<'=;0)(/"%;>'?4;%0@''
claude.payri@ird.fr
2'7;+%A+'=)"$-)'B/-'?"3%-/"4)"$'C'D&#$;%";E0)'1)3)0/.4)"$'F78=?GD1H5'I,)'J"%3)-#%$K'/B'$,)'D/&$,'
''7;+%A+5'7>L>'6/M'NNOP'5'D&3;5'Q%R%
3'7-)#)"$';((-)##@'J"%3)-#%$K'/B'=;.)'I/<"5'6/$;"K'1).;-$4)"$';"('S;-%")'*)#);-+,'!"#$%$&$)5'=;.)'
Town, South Africa
BENTHIC ALGAL AND SEAGRASS COMMUNITIES IN BAA ATOLL,
MALDIVES
BY
CLAUDE E. PAYRI,1 ANTOINE D.R. N’YEURT,1,2 AND LYDIANE MATTIO1,3
ABSTRACT
I,)'.-)#)"$'#&-3)K'<;#'&"()-$;T)"'$/'.-/3%()'$,)'A-#$'+)"#&#'/B'$,)'4;-%")'
U/-;'F4;+-/;0V;)';"('#);V-;##)#H'/B'6;;'8$/005'/")'/B'$,)'WO'S;0(%3%;"';$/00#5';"('$/'
serve along with the macro-fauna biodiversity inventories for conservation purposes.
Species collection and inventories have been conducted at 27 sites covering the widest
selection of habitats recognized based on satellite images including islands shorelines,
-))B'U;$#5'B;-/#5'.;$+,'-))B#5'.;##)#';#'<)00';#'#,;00/<';"('()).'/&$)-'-))B'#0/.)#>'8'
total of 405 specimens were collected and 176 species representing 10 Phaeophyceae,
9P'=,0/-/.,K$;5'NXP'*,/(/.,K$;';"('$</'#);V-;##)#'<)-)'%()"$%A)(>'I,)'0;V//"'.;$+,'
reefs and the oceanic reef slopes were the most diverse geomorphological habitat types
and displayed the highest species richness with 38 spp. All lagoon sites shown a similar
richness compared to each other with an average species number of 26 spp, while the
()).'0;V//"'U//-';"('$,)'#);V-;##'E)(#'%"'/+);"%+G)M./#)('-))B'U;$#'<)-)'$,)'0)##'
species-rich habitats. The most common species, occurring at all visited sites, were
Tydemania expeditionis and Halimeda minima and the most species rich genera appeared
to be Halimeda and Caulerpa. No community structure nor strongly supported species
assemblages associated to geomorphological habitat types was found.
Previous lists available for other Maldivian atolls listed 208 algal species. Sixty
of these records were found in Baa Atoll while 113 of the species recorded in the present
study represent new records for the Maldives bringing the total number of algal species
$/'YWN>'I,)'-)#&0$%"V'#.)+%)#'0%#$'#,/<#'$,;$'$,)'S;0(%3%;"';0V;0'U/-;'%#'$K.%+;00K'$-/.%+;0'
;"('4/#$'/B'$,)'#.)+%)#'E)0/"V'$/'$,)'!"(/G7;+%A+'E%/V)/V-;.,%+'.-/3%"+)>'!"'$,%#'.;.)-5'
we give a general description of the representative macrophyte communities of Baa Atoll
in relation to the geomorphology of reefs.
32
INTRODUCTION
Z)-K'0%4%$)('%"B/-4;$%/"'%#';3;%0;E0)'/"'S;0(%3)#';-+,%.)0;V/'4;-%")'U/-;'
despite a large number of oceanographic expeditions carried out in the region. Most
/B'$,)'-)+/-(#';-)'E;#)('/"'#./-;(%+'#$&(%)#>'I,)'A-#$'.,K+/0/V%+;0'$;M/"/4%+'-)+/-(#'
were published from the limited biological material collected during the expeditions of
[>D>'\;-(%")-'%"'$,)');-0K'N]XX#'F\;-(%")-5'N]XYH';"('#$&(%)('EK'6;-$/"'FN]XYH5'Q/#0%)'
FN]XY5'N]X^H5';"('_)E)-';"('Q/#0%)'FN]X`H>'I,)'D);0;-T'?M.)(%$%/"'%"'N]X9'-)#&0$)('%"'
\)..';"('\)..a#'FN]X`H';"('_)E)-G3;"'6/##)a#'FN]N`H'-)+/-(#'/B'#/4)'=,0/-/.,K$;'
FbV-))"';0V;)cH';"('*,/(/.,K$;'Fb-)(';0V;)cH>':)<$/"'FN]9YH'.&E0%#,)('/"0K'/")'
#);<))('-)+/-('B-/4'$,)'[>'S&--;K')M.)(%$%/"'N]YYGN]Y`>'8$'$,%#'$%4)'$,)'T"/<0)(V)'
/B'$,)'S;0(%3%;"';0V;0'U/-;'<;#'-)#$-%+$)('$/'W`'#.)+%)#'%"+0&(%"V'N^'*,/(/.,K$;5'A3)'
Chlorophyta and two Pheaophyceae (“brown algae”). During the expedition led by D.R.
D$/((;-$'B-/4'=;4E-%(V)'%"'N]O`5'D%V))'FN]OOH'#;4.0)('0;"(';"('4;-%")'3)V)$;$%/"'
at Addu Atoll. The preliminary results of the Addu Atoll expedition were published
in Atoll Research Bulletin'EK'D$/((;-$'FN]OOH>'I,)'D%V))'+/00)+$%/"'<;#'#$&(%)('EK'
I#&(;';"(':)<,/&#)'FN]OOH'<,/'.&E0%#,)(';'$;M/"/4%+'0%#$5';((%"V'#%V"%A+;"$0K'$/'
the total species number of macroalgae with 37 Rhodophyta, 30 Chlorophyta , nine
Phaeophyceae and seven cyanobacteria (“bluegreen algae”). Extensive collections of
benthic macroalgae were made at nine Maldivian atolls during Cruise B and Cruise 5
of the R/V Te Vega'?M.)(%$%/"#'%"'N]O`'EK'd>?>'d;+T)$$';"('S>[>'_K"")'-)#.)+$%3)0K>'
d;+T)$$'FN]O]H'#$&(%)(',%#'/<"'+/00)+$%/"'B/-',%#'7,1'(%##)-$;$%/"';#'<)00';#'4;$)-%;0'
+/00)+$)('EK'=>'*,K")'%"'N]O^';$'8((&'8$/00'(&-%"V'$,)'J>D>':;3K'6%/0/V%+;0'?M.)(%$%/"'
to the Chagos Archipelago. Based on these collections additional records were published
%"'d/00)"E)-Va#'FN]OP;5'EH'4/"/V-;.,#';"('8-)V//(';"('d;+T)$$'FN]^NH'()#+-%E)(';'
new species of Rhodophyta (Dictyurus maldiviensis'd;+T)$$'C'8-)V//(H>'e;$)-5'd;+T)$$'
FN]^^H'.&E0%#,)('$,)'4/#$'+/4.-),)"#%3)'+;$;0/V&)'/B'$,)'S;0(%3%;"'4;-%")';0V;)'
with 248 records including 136 Rhodophyta, 74 Chlorophyta, 17 Phaeophyceae and 21
=K;"/E;+$)-%;>'8'"&4E)-'/B'$,)#)'-)+/-(#',/<)3)-'<)-)'%()"$%A)('/"0K';$'$,)'V)"&#'
0)3)0>'8'K);-'0;$)-5'I%$0K;"/3;';"('6&$/-%"'FN]^PH'.&E0%#,)(';'#,/-$'0%#$'/B'4;+-/;0V;)'FNP'
$;M;H'B-/4'$</';$/00#'/B'$,)'S;0(%3)#>'Q%";00K'_K"")'FN]]YH'.&E0%#,)(';'0%#$'/B'9X'#.)+%)#'
based on his own collections including the description of Bangia halymeniae Wynne
from Malé Atoll.
!"'WXX]5'E)B/-)'$,)'6;;')M.)(%$%/"5'$,)'4/#$'&.(;$)('+/4.%0;$%/"'/B'$,)'4;-%")'
U/-;'/B'$,)'S;0(%3)#'<;#';3;%0;E0)'B-/4'b;0V;)E;#)>+/4c';"('0%#$)('NWX'*,/(/.,K$;'5'^X'
Chlorophyta, 18 Phaeophyceae and 21 Cyanobacteria records (Guiry and Guiry, 2011).
I,)'.-)#)"$'#&-3)K'<;#'&"()-$;T)"'$/'.-/3%()'$,)'A-#$'+)"#&#'/B'$,)'4;-%")'
U/-;'/B'6;;'8$/00';"('$/'#)-3)';0/"V'<%$,'$,)'4;+-/GB;&";'E%/(%3)-#%$K'%"3)"$/-%)#'B/-'
+/"#)-3;$%/"';"('%()"$%A+;$%/"'/B'E%/(%3)-#%$K',/$G#./$#'Fd;4)0';"('8"(-2B/&f$5'$,%#'
issue). We also provide here a general description of the representative macrophyte
communities of Baa Atoll in association with the geomorphology of reefs.
33
SAMPLING SITES AND METHODS
Baa Atoll is situated in the Northern Indian Ocean at latitude 5°11'N and longitude
^Wg9]h?>'6;;'%#'/")'/B'$,)'WO'S;0(%3%;"';$/00#'#$-)$+,%"V'%"';'"/-$,G#/&$,'(%-)+$%/"'/BB'
India’s Lakshadweep islands. It stands in the Laccadive Sea, about 700 km south-west
of Sri Lanka and 400 km south-west of India. Baa Atoll is 42 km long and 32 km wide.
I,)'$-/.%+;0'+0%4;$)'%#'+/4./#)('/B'$</'4;%"'#);#/"#@'$,)'(-K'#);#/"';##/+%;$)('<%$,'$,)'
winter north-eastern monsoon and the rainy season with strong winds and storms.
I,)'.-)#)"$';0V;0'U/-;';"('#);V-;##'%"3)#$%V;$%/"'/B'6;;'8$/00'<;#';+,%)3)('
(&-%"V'S;K';"('[&")'WXX]'R&#$';B$)-'$,)'4/%#$'#/&$,G<)#$'4/"#//">'D&-3)K#'<)-)'
conducted at 27 sites (Fig. 1) covering the widest selection of habitats recognized based
/"'#;$)00%$)'%4;V)#'%"+0&(%"V'%#0;"(#'#,/-)0%")#5'-))B'U;$#5'B;-/#5'.;$+,'-))B#5'.;##)#'
as well as shallow and deep outer reef slopes. Most of the sites were prospected by
D=J68'B-/4'9X'4'$/'$,)'#&-B;+)>'I,)'#,;00/<';-);#'%"+0&(%"V'B-%"V%"V'-))B'U;$#5'.;$+,'
reefs and shorelines were sampled by snorkelling or reef walk. The sampling effort was
standardized and inventory duration at each site was set to 80 min.
All specimens collected were sorted, pressed and air-dried as herbarium vouchers.
Photographs of collected specimens were taken in-situ and referenced according to
herbarium accessions. Samples of selected specimens were pickled in a solution of
buffered formalin in seawater (5%) for further anatomical studies. Samples from a
selection of taxa were preserved in silicagel or ethanol for further DNA analyses. Since
all herbarium specimens were air dried (no formalin), DNA extraction is feasible for
further studies if necessary. DNA samples of Dictyotales (Dictyota J.V. Lamouroux and
Padina Adanson) and Halimeda J.V. Lamouroux have already been processed and will be
included in regional phylogenetic studies.
Overall, specimens were collected to represent a baseline taxonomical collection
for the area and the species inventory was compiled in order to reach the more
comprehensive species list for Baa Atoll. In agreement with the Maldive Research Center
(MRC), the collection was deposited in the phycological herbarium of IRD (Institut de
Recherche pour le Développement) in Nouméa (IRD-NOU), New Caledonia.
RESULTS
Representative Algal Communities and Associated Habitats
D)3)"'+0;##',;E%$;$#',;3)'E))"'()A")('E;#)('/"'V)/4/-.,/0/VK';"('4/#$'/B'$,)4'
were prospected. All habitats could not be sampled with the same effort and some of
$,)45'#&+,';#'#);V-;##'E)(#'/-'/+);"%+'-))B'U;$#5'<)-)'/"0K'3%#%$)('/"+)'FI;E0)'NH>'
During the present investigation 405 specimens were collected from 27 sites
FQ%V>'NH>'8'$/$;0'/B'N^O'#.)+%)#'<)-)'%()"$%A)(';"('-).-)#)"$)('NX'7,;)/.,K+);)5'9P'
=,0/-/.,K$;5'NXP'*,/(/.,K$;'i:6@'/"0K'$,)'4/#$'+/44/"'-)('+/-;00%")#';0V;)'<)-)'
+/"#%()-)(j';"('W'#);V-;##)#>'I,)'$;M/"/4%+'+0;##%A+;$%/"'&#)('(&-%"V'$,%#'</-T'
followed
The catalogue of the benthic marine algae of the Indian Ocean by Silva and
+/G;&$,/-#'FN]]OH>
The species list is given in Appendix 1. Records belong to 17 orders,
Y9'B;4%0%)#';"(']`'V)")-;'FI;E0)'WH>
34
Class
Habitat
Oceanic
reef flat
(seagrass)
Lagoon
reef flat
and slope
Lagoon
patch reef
Lagoon
reef flat
Deep
lagoon
Oceanic
reef flat
Oceanic
reef slope
number
of sites
(1)
(10)
(5)
(3)
(1)
(2)
(5)
Site
label
2
1, 5, 6, 8,
12, 13, 21,
22, 24, 28
10, 11,
N^5'N]5'W9
3, 16, 20
23
N95']
4, 7, 14,
18, 27
Figure 1. Location of the sampling sites in Baa Atoll.
I;E0)'N>'D;4.0%"V'#%$)#'(%#$-%E&$%/"'%"'$,)'#)3)"',;E%$;$'+0;##)#'()A")('E;#)('/"'
geomorphology.
35
S/#$'/B'$,)'#.)+%4)"#',;3)'E))"'%()"$%A)('$/'#.)+%)#'0)3)0'FP9'k'/B'$,)'
+/00)+$%/"H5'E&$'#/4)'/B'$,)'#.)+%4)"#'FN9'k'/B'$,)'+/00)+$%/"H'-)4;%"'&"%()"$%A)('B/-'
lack of reproductive parts or poor sampling. In addition the two seagrasses Syringodium
isoetifolium (Ascherson) Dandy and Thalassia hemprechii (Ehrenberg) Ascherson have
been observed forming beds in only a single location (Baa2, Fig.1).
The most species rich genera appeared to be the green algae Halimeda and
Caulerpa J.V. Lamouroux, however surprisingly, no bulbose Halimeda spp. were
recorded during this survey nor the large Fucales such as Sargassum C. Agardh. All the
#.)+%)#'#;4.0)('(&-%"V'$,)')M.)(%$%/"'<)-)';##/+%;$)('$/',;-('#&E#$-;$&4')M+).$'/")@'
Boodleopsis pusilla FQ>D>'=/00%"#H'_>*>'I;K0/-5'8>6>'[/0K'C'6)-";$/<%+l'<,%+,'/++&--)('
on faros’ sandy bottoms. (Appendix 2).
Species Richness Distribution in Baa Atoll.
Species richness per site. Species richness per site (Fig. 2) ranged from two at
Baa 23 (deep lagoon) to 38 species at Baa 11 (lagoon patch reef) and Baa 7 (oceanic reef
slope) (Fig. 1). These two sites, coral built and exposed to strong water movements, were
the most diverse and displayed the highest species richness with 38 spp.
I;E0)'W>':&4E)-'/B'L-()-#5'Q;4%0%)#5'\)")-;';"('D.)+%)#'/B'4;+-/.,K$)#'%()"$%A)('B-/4'
Baa Atoll
Orders
Families
Genera
Species
Rhodophyta
10
22
64
108
Macroalgae
Chlorophyta
5
11
25
58
Phaeophyceae
2
2
5
10
TOTAL
17
35
]`
176
Seagrasses
Magnoliophyta
1
2
2
2
Figure 2. Distribution of species richness per sites.
36
Because only two species have been collected from the sandy bottom of the
()).)#$'0;V//"'#%$)'F6;;'WY5'9X'4'()).H';"('$,;$'6;;'WX'F0;V//"'-))B'U;$H'<;#'"/$'
properly prospected (no SCUBA on the deeper part), we believe that the data are not
reliable enough to report on the species richness of corresponding habitats. The seagrass
bed (Baa 2) housed few algal species (four spp, including two coralline rhodoliths).
I,)'#;"(K',;E%$;$#'F6;;']5'NY5'NOH';"('$,)'-))B'U;$#'F6;;'P5'NW5'N9H'<%$,'0/<)-'E%/$/.)'
(%3)-#%$K'/-')M./#)('$/'3)-K'#$-/"V'+&--)"$'F6;;'N^5'N]H'#,/<)('4/()-;$)'#.)+%)#'
richness (from 11to 24 spp). For all the other sites algal richness varied between 25 and
35 species (Fig. 3).
Species richness per geographic areas. The main features of Maldivian reef
+/4.0)M'+;"'E)'+0;##%A)('%"$/'$</'4;R/-'+0;##)#@'F%H'$,)'A-#$'+0;##'%"+0&()#'$,)';$/00'-%4'
4;()'/B'B;-/#'<%$,')"+0/#)('0;V//"#'()0%4%$)('EK'0;-V)'#);<;-('-))B'U;$#5'()).'/&$)-'
reef slopes, forereefs, inner slopes and channels/passes; (ii) the second class includes
$,)'0;V//"'#$-&+$&-)#'<%$,'4/#$0K'B;-/#';"(')"+0/#)('0;V//"#5'-))B'U;$#5'-))B'.;$+,)#5'
pinnacles and deep lagoon sections.
No contrasting spatial variation could be observed between the different sections
of the atoll rim (Table 3). The sampling effort in each geographic area was not strictly
similar and could partially affect the resulting values. The average species richness did
not contrast strongly from North (21 spp.) to South (28 spp.) and from East (26.2 spp.)
to West (27 spp.). Nevertheless, the lowest species richness was observed in the northern
rim section. No contrasting difference could be found between the average species
richness of the global atoll rim (25.2 spp.) and the lagoonal faros (24.7 spp.).
Figure 3.Spatial distribution of the species richness in Baa Atoll.
37
Species richness per geomorphological habitat type. Average species richness
varied within each geomorphological habitat type (Fig. 4). Figure 4 shows that the deep
0;V//"';"('$,)'#);V-;##'E)(#'%"'/+);"%+'-))B'U;$#'<)-)'$,)'0);#$'#.)+%)#'-%+,',;E%$;$#5'
while these sites were also the least sampled (n=1 site for each of them). All lagoon sites
showed a similar richness compared to each other with an average species number of 26
spp. but different sampling efforts (n= 3'#%$)#'B/-'$,)'m0;V//"'-))B'U;$a5'n=10 sites for the
m0;V//"'-))B'U;$';"('#0/.)a';"('n= 5 sites for the ‘lagoon patch reef’). The oceanic slope
showed an average of 30 spp. for the 5 sites.
The spatial distribution of the species varied with bathymetry and some
species were observed at a wide range of depths. This is true for instance for the green
algae Caulerpa diligulata, Halimeda discoidea, Rhipidosiphon javensis, Tydemania
expeditionis and the red Botryocladia which were found from 5 m down to 40 m,
independently of geographical location. Other species were found to be restricted to deep
l/")#5'#&+,';#@'Padina okinawensis, Cladophora feredayoides, Microdictyon okamurae,
Caulerpa sedoides, or cryptic and only in shaded areas such as Cryptonemia umbraticola
or Corynocystis prostrata. Many other species were restricted to shallow waters such as
Valonia aegagropila, Dictyurus purpurascens, Halymenia actinophysa, Hypnea spp. and
Turbinaria ornata.
Table 3. Species richness per geographic area (sites 2 and 20 were excluded because not
properly prospected)
Geographic Area
Number of sites
Northern
Rim
(4)
Southern
Rim
(3)
Eastern
Rim
(5)
Western
Rim
(2)
Atoll Rim
(14)
Atoll
Lagoon
(8)
Site label (BaaX)
14, 15,
16, 17
1, 3, 4
^5'P5']5
NP5'N]
27, 28
1, 3, 4, 7,8,
]5'N`5'N95
16, 17, 18,
N]5 27, 28
5, 6,10,
11,12,13,
21, 22, 23,
24, 25
Average species
21
28
26.2
27
25.2
24.7
Figure 4. Variation of species richness per habitat type.
38
Species rarity. Patterns of the algal vegetation in the Baa Atoll were characterized
by the dominance of species with very low occurrences at all the prospected sites (Fig. 5).
Half of the species (n=87) were found in less than 8 % (2/27) of the sites thus revealing
;',%V,'E)$;G(%3)-#%$K>':/'#.)+%)#'<)-)'.-)#)"$';$');+,'/B'$,)'W^'#%$)#>'I,)'4/#$'B-)n&)"$'
species were the Chlorophyta Tydemania expeditionis Weber-van Bosse occurring in
20/27 sites and Halimeda minima F_>*>I;K0/-H'd%00%#G=/0%"3;&MH'.-)#)"$'%"'N]oW^'#%$)#>'
Ninety percent of the species occurred in only 13 sites which represents less than half of
the prospected sites. Less than 10% of the species were represented by a single specimen.
Main Algal Assemblages.
The most common species are illustrated in Appendix 3.
!"#$"%&'#'($()*+%*+%"$#**+%,''-%.$(/%$+0%/"*1'/2%The algal communities of the
e;V//"'-))B'U;$#';"('#0/.)#';++/&"$'B/-';'0;-V)'"&4E)-'/B')"+-&#$%"V'+/-;00%")';0V;)>'
They are mostly represented either by Hydrolithon onkodes which develops thick crusts
and a candle-like Hydrolithon sp., or branched clumps of Lithophyllum kotschyanum
4%M)('<%$,'#)3)-;0'U)#,K'#.)+%)#'V-/<%"V'%"'+/-;0'+-)3%+)#>'L"'$,)'-))B'U;$#5'4;"K'
species (mostly red algae) grow under the branches of corals. They include the large
spreading mats of Dictyurus purpurascens, Hypnea pannosa and Hypnea spinella,
isolated clumps of 3$"$4$5,$%6"$7'+(*/$, Actinotrichia fragilis, or the delicate and
frondose Halymenia durvillei. The green algae were well represented with Tydemania
expeditionis and several Halimeda spp. including the very common and abundant
H. minima, H. opuntia and H. gracilis (with tiny segments) while the larger species
H. distorta and H. discoidea were common features of the reef slope’s deeper parts.
Figure 5. Histogram of species occurrences at the 27 sites.
Y]
Some branched Codium geppiorum were also observed. Dead corals were colonized
by turfs of Gelidiopsis intricata, Champia vieillardii and Caulerpa nummularia. The
vegetation on the slopes was scarce, less abundant and dominated by calcareous species
such as Lithothamnium proliferum and Halimeda gracilis. Fleshy algae were less
abundant and mostly represented by Gibsmitha hawaiiensis, G. dotyii, and Botryocladia
skottsbergii,Chamaebotrys boergesenii and Portieria hornemanii. Various thin and
small fronds of the dark green algae Rhipiliella spp. and Rhipiliopsis spp. formed small
associations in the shady areas with Corynocystis prostrata Kaft and Cryptonemia
umbraticola. The Caulerpa spp. were poorly represented in these environments and
Phaeophyceae were mainly represented by small Dictyotales such as Dictyota friabilis
and Dictyopteris repens. The large Fucales Turbinaria ornata was very rarely found and
represented only by juveniles while no Sargassum species were observed.
!"#$"%&'#'($()*+%*+%"$#**+%,''-%.$(/2'I,)'#,;00/<'-))B'U;$#'%"'$,)'0;V//"';..);-)('
heterogeneous and some of them in the south-west of the atoll (Baa 3, Fig. 1) showed
much more species richness and biomass than those located in the north-eastern section
of the atoll. H. micronesica and H. taenicola were observed only in the north (Baa 20).
I,)'3)V)$;$%/"';##)4E0;V)'<;#'#%4%0;-'$/'$,;$'/B'$,)'0;V//"'-))B'U;$#'<%$,'"&4)-/&#'
encrusted corallines including Hydrolithon onkodes, the candle-like Hydrolithon sp. and
numerous rhodoliths of Hydrolithon reinboldii. Various articulated coralline species such
as Amphiroa spp. formed clumps on the reef top.
Thin and delicate Rhodophyta such as Hypoglossum spp., Nitophyllum spp. and
several Laurencia spp., were observed in the crevices of hard substratum along with
the very abundant green fan-like Rhipidosiphon javensis, the bright green Anadyomene
wrigthii and Rhipiliella verticillata. The typical fan-like Lobophora variegata and several
large Dictyota spp. were found growing on dead corals along with the green sponge-like
Boodlea composita and the plumose dark green Bryopsis pennata.
Algal vegetation in lagoon patch reefs. The species assemblages and richness
observed in lagoon patch reefs were relatively variable from one site to another with an
;3)-;V)'/B'W9'#..>'S/-)'$,;"',;0B'/B'$,)'#.)+%)#'<)-)'.-)#)"$';$'0);#$'$,-))'/&$'/B'A3)'
sites visited in this same geomorphologic habitat type. The assemblage was dominated by
large green Tydemania expeditionis, as well as Halimeda minima and H. opuntia with a
lesser abundance of by H. cuneata and H. gracilis, the bright green pompom-like Chlo-
rodesmis fastigiata, the dark green Avrainvillea lacerata and Asteromenia anastomosans.
Caulerpa diligulata /++&--)(';$';00'#%$)#'+0;##%A)('%"'$,%#'V)/4/-.,/0/V%+;0',;E%$;$'$K.)>'
Most of the investigated sites showed turf assemblages associated with dead coral includ-
ing mostly Gelidiopsis intricata, Dictyota humifusa, and Champia compressa. Several
species such as !8$+(9*19*,$%1$8)68$, Caulerpa diligulata, Cladophoropsis vaucheri-
aeformis, C. herpestica were also common component of the oceanic reef slopes assem-
blages which are described hereafter.
Algal vegetation of the oceanic reef slope. The species assemblages associated
<%$,'$,)'/&$)-'-))B'#0/.)';..);-)('$/'E)'$,)'4/#$'(%3)-#)';"('-%+,5')3)"'%B'$,)'U)#,K'#.)-
+%)#'<)-)'"/$'3)-K'(%3)-#%A)(>'8E/&$'YX'#.)+%)#'<)-)'/E#)-3)('%"'4/#$'/B'$,)'#%$)#>'I,)'
40
vegetation was dominated by coralline species especially on the upper part of the slope.
Some sections of the outer reef slope were very steep or vertical walls with numerous
crevices, overhangs and small caves. Coral walls were encrusted by coralline species and
Peyssonnelia spp. picturing an attractive mosaic of forms and colors. Lithothamnion pro-
liferum was easily recognizable thanks to its pink crust and numerous short knobs. Along
the slope several Rhodymeniales including Leptofauchea spp. and Rhodymenia spp. oc-
curred in caves and crevices as well as Cryptonemia umbraticola, Corynocystis prostrata,
the iridescent Halichrysis irregularis and the star–shaped Asteromenia anastomosans.
Numerous small green species such as Phyllodictyon anastomosans, Rhipidosiphon ja-
vensis and Rhipilia crassa were present in the crevices while Cladophora feredayoides
and Caulerpa sedoides were collected from rubbles. Conversely the large Gibsmithsia
hawaiiensis and G. dotyii as well as the delicate Kallymenia thompsonii, Dasya anasto-
mosans and D. baillouviana remained scarce. The most obvious species were the green
Halimeda spp. (H. gracilis, H. minima and H. cuneata) and Tydemania expeditionis.
Apart from Caulerpa diligulata, which was relatively abundant, the other species of
Caulerpa (:2%6")8*)0'/ and C. sedoides) were very inconspicuous.
!"#$"%&'#'($()*+%*-%(9'%*8'$+)8%,''-%.$(2%L+);"%+'-))B'U;$#'<)-)'"/$'#&-3)K)(';#'
B-)n&)"$0K';#'$,)';E/3)'()#+-%E)(',;E%$;$#';"(';-)'-).-)#)"$)('%"'$,%#'#$&(K'EK'/"0K'$</'
sites. The species richness was similar from one site to the other with an average of 12
species. Species assemblages however differed strongly. Only two species were common
$/'E/$,'#%$)#@'$,)'3)-K'<%()#.-);('Halimeda opuntia ;"('$,)'_)#$'7;+%A+'Padina okinaw-
ensis. Considering the low sampling effort applied to this geomorphological habitat type
(&-%"V'$,)'#&-3)K5'"/'()A"%$%3)'B);$&-)#'+;"'E)'()#+-%E)(',)-)>'
Algal vegetation associated to seagrass beds. D);V-;##)#';-)'U/<)-%"V'.0;"$#'E)-
longing to the Cymodoceaceae and Hydrocharitaceae families which are currently classi-
A)('%"'$,)'/-()-'80%#4;$;0)#'F"/4)"+0;$&-)'E;#)('/"'.,K0/V)")$%+'#$&(%)#'87\!!!5'WXX]H>'
In tropical regions, they are almost permanently immersed in sheltered marine and estua-
rine biotopes which offer a suitable substrate for rooting in mud, sand or coarse rubble. In
some instances they may also develop into large meadows or beds in deeper lagoon parts
down to 40 m deep, or on barrier reefs surrounding lagoon islands. They are remarkable
habitats in tropical shallow waters and they often represent keystone ecosystems on sandy
bottoms and along shorelines between mangroves and coral reefs.
In Baa, only one site showing typical seagrass habitat was surveyed (oceanic
-))B'U;$5'6;;'WH>'I,)'#);V-;##'#.)+%)#'(%3)-#%$K'<;#'n&%$)'0/<'<%$,'/"0K'$</'#.)+%)#@'
Syringodium isoetifolium and Thalassia hemprechii, forming a dense bed in an area
exposed to strong currents. The algal vegetation associated to this meadow was very poor
with only four large species including Halimeda opuntia, Valonia aegagropila and two
-,/(/0%$,GB/-4%"V'+/-;00%")';0V;)@'Neogoniolithon frutescens and N. laccadivicum.
More prospection is needed to assess the status of seagrass beds in Baa Atoll.
41
DISCUSSION
S;-%")'S;+-/.,K$)#'%"'6;;@'\)")-;0'!"#%V,$#>
8'$/$;0'/B'N^`'4;+-/;0V;0'#.)+%)#'<)-)'%()"$%A)('B-/4'$,)'#&-3)K'/B'6;;'
Atoll. This result does not include the full diversity of coralline algae especially for
the encrusting forms which were not fully sampled in the present study. This group
%#'$;M/"/4%+;00K'(%BA+&0$';"(';'4/-)'+/4.-),)"#%3)'%"3)"$/-K'%#'"))()('$/'.-/.)-0K'
describe its diversity in Baa. Similarly, microscopic epiphytes and epilithic species
have not been exhaustively sampled and studied. A more focused study would most
probably reveal a higher diversity. Nevertheless, our results document and acknowledge
$,)')+/0/V%+;0'-;-%$K'$K.%+;0'%"'$-/.%+;0')+/#K#$)4';#'<)00';#'+/"A-4'.-)3%/&#'#$&(%)#'
conducted in coral reef environments on biodiversity of molluscs and crustaceans
(Bouchet et al., 2002). Overall, and in the framework of the Baa expedition, taxonomic
-)#&0$#5'#.)+%)#'(%#$-%E&$%/"';"('/++&--)"+)#'/E$;%")('B/-'$,)'4;-%")'U/-;';-)'#%4%0;-'$/'
those obtained for the other marine groups studied during this expedition (cf. this issue of
Atoll Research Bulletin).
We carried out a multivariate analysis based on species absence/presence within
$,)'W^'#$&(%)('#%$)#'F-)#&0$#';3;%0;E0)'&./"'-)n&)#$'$/'$,)'A-#$';&$,/-H>'*)#&0$#'#,/<)('
"/'+/44&"%$K'#$-&+$&-)'/-'#$-/"V'%"(%+;$%/"'/B'#.)+%A+'#.)+%)#';##)4E0;V)#';##/+%;$)('
to geomorphological habitat type. This relative homogeneity could be explained by
limited habitat diversity. From its geographical location, Baa atoll appears greatly
%"U&)"+)('EK'#,%B$%"V'4/"#//";0'/+);"%+'+/"(%$%/"#>'I,%#'+/&0('V)")-;$)',/4/V)")/&#'
environmental forcing thus limiting habitat diversity and in turn leading to a more or
0)##',/4/V)")/&#0K'(%#$-%E&$)('U/-;';$'$,)';$/00'#+;0)>'8$'-))B'#+;0)')"3%-/"4)"$;0'
factors are not strictly homogeneous and benthic community assemblages may show
spatial heterogeneity (Vroom et al. 2005) which could be the case in Baa. Here, no
#%V"%A+;"$'(%BB)-)"+)'%"'$,)'#.)+%)#'-%+,")##'/B'$,)'4;-%")'U/-;',;#'E))"'#,/<"';4/"V'
the different areas of the atoll, however the number of restricted species was much higher
$,;$'$,)'"&4E)-'/B'#.)+%)#'<%()0K'(%#$-%E&$)(>'I,%#'-)#&0$'n&)#$%/"#'<,)$,)-'4;+-/;0V;0'
communities within a same geomorphological area are ecologically similar.
=K+0/")#';"('E0);+,%"V')3)"$#';-)'#%V"%A+;"$'(%#$&-E;"+)#'-)#&0$%"V'./$)"$%;00K'%"'
;'#,%B$'B-/4'+/-;0'(/4%";$)('$/'4;+-/;0V;)'(/4%";$)('-))B#'FS+=//T5'N]]]p'6)00<//('
et al., 2006). However no evidence of algal dominated communities was observed during
$,)')M.)(%$%/"5'+/"(&+$)('NN'K);-#';B$)-'$,)'4;##%3)'N]]P'E0);+,%"V')3)"$'$,;$'%4.;+$)('
Maldives.
Previous lists available for other Maldivian atolls (Guiry and Guiry, 2011) listed
208 algal species. Sixty three of these records were found in Baa Atoll. Conversely, 113
of the species recorded in the present study represent new records for the Maldives,
E-%"V%"V'$,)'$/$;0'"&4E)-'/B';0V;0'#.)+%)#'$/'YWN'FWXX'*,/(/.,K$;5']^'=,0/-/.,K$;';"('
24 Phaeophyceae). Comparison with previous studies undertaken in the Maldives show a
narrow overlap of the diversity of the species between the different atolls studied.
As observed from the literature and from this study, the Maldivian macroalgal diversity
varies from one atoll to another and several very common tropical species have not been
42
recorded during the present survey. Some of the species are seasonal (e.g. Rosenvingea
intricata) and did not occur in May-June at the time of the survey. Another likely
hypothesis is that Baa Atoll does not offer the suitable habitats that support those
particular species.
Biogeography
' I,)'#.)+%)#'0%#$')#$;E0%#,)('B-/4'$,%#'#&-3)K'#,/<#'$,;$'$,)'S;0(%3%;"';0V;0'U/-;'
%#'$K.%+;00K'$-/.%+;0';"('4/#$'/B'$,)'#.)+%)#'E)0/"V'$/'$,)'!"(/G7;+%A+'E%/V)/V-;.,%+'
.-/3%"+)>'D)3)-;0'#.)+%)#'()#+-%E)('B-/4'$,)'7;+%A+'-)V%/"'<)-)'-)+/-()('B/-'6;;'(&-%"V'
$,%#'#$&(K';"('-).-)#)"$'$,)%-'A-#$'-)+/-('B/-'$,)'!"(%;"'L+);">'I,)K';-)'B/-')M;4.0)'
the Dictyotales Padina okinawensis described from Southern Japan, the Delesseriaceae
Myriogramme heterostroma and M. melanesiensis originally described from the Solomon
!#0;"(#';"('Z;"&;$&'F_)#$)-"'7;+%A+H';"('$,)'d;0%4)(;+);)'Halimeda xishaensis from
China (Gulf of Tonkin). This suggests that the species geographic distribution is broader
$,;"'/-%V%";00K'$,/&V,$';"('&"()-0%")#'$,)'E%/V)/V-;.,%+';BA"%$%)#'/B'$,)'S;0(%3)#'4;-%")'
U/-;'<%$,'$,)'$-/.%+;0'_)#$'7;+%A+>
=/4.;-%#/"'<%$,'U/-;#'B-/4';(R;+)"$'-)V%/"#'%#'0%4%$)('(&)'$/'(%BB)-)"+)'%"'
sampling effort and lack of recently revised species lists. However we compared different
archipelogoes from the West Indian Ocean based on species lists available at algaebase.
com (Table 4). The proportion of species shared by Baa and other atolls/islands of the
Maldives, Laccadives, Chagos, Seychelles and La Reunion was 35.7, 25.5, 17.6, 43.1 and
W]>9k'-)#.)+$%3)0K>'I,)',%V,)#$'.)-+)"$;V)'#%4%0;-%$K';..);-)('$/'E)'<%$,'$,)'D)K+,)00)#'
Islands and the other Maldivian atolls. The lowest similarity was observed with the
Laccadives (10.57° N and 72.62° E) and Chagos (6° S and 72° E). The reason for such a
low similarity despite the geographical location of these Islands (Chagos and Laccadives
are located about 600 km off the south and about 250 km off the north of the Maldives,
respectively), could be explained by low collecting efforts at these localities resulting in
incomplete species lists. A Sorensen’s Similarity Index was calculated between the Baa
4;-%")'U/-;'+/4./#%$%/"';"('$,/#)'/B'$,)'/$,)-'0/+;0%$%)#'FI;E0)'`H>'I,)',%V,)#$'3;0&)#'
were observed for the other Maldivian atolls (0.24). SI values were mostly low and
%00&#$-;$)';'#.)+%)#'(%3)-#%$K'#.)+%A+'$/');+,'/B'$,)'(%BB)-)"$';-);#'+/"#%()-)(>'8'"&4E)-'
of species were not observed in Baa; including Phaeophyceae taxa, among which several
species of Turbinaria and Sargassum. This latter genus was not observed in Baa atoll
during the present study nor has it been reported before. Nevertheless, several Sargassum
species have been mentioned by MRC staff and drift specimens have been collected from
other Maldivian atolls. The reason why species of this widespread genus is missing from
the Baa inventory warrants further investigation. Grazing pressure, seasonality or very
restricted distribution within Baa atoll (i.e. unprospected sites) are plausible hypotheses.
The absence of Sargassum /"'7;+%A+';$/00#'<;#'A-#$'(%#+&##)('EK'1/$K'FN]9`H>'I#&(;'
FN]^OH'()#+-%E)('$,)'.-)#)"+)'/B'S. crassifolium'/"'$</'7;+%A+';$/00#5'J0%$,%'8$/00'
(Yap State) and Kayangel Atoll (Palau); later Hodgson and McDermid (2000) reported
Sargassum sp. on Ant Atoll (Pohnpei State). Sterile plants were found in January at
Kayangel and fertile plants were found in June and July at Ulithi. The interesting fact is
43
that all Sargassum were collected on the northeast (windward side) of the atolls (Tsuda
com.pers.).It is interesting that the relative absence of Sargassum on Indian Ocean atolls
%#'#%4%0;-'$/'+;#)#'%"'$,)'7;+%A+'L+);">
Finally, our results address the issue of representativeness, which is critical in
biodiversity management. The little overlap of the macroalgal assemblages between
the different atolls demonstrates that, even at small biogeographical scales the spatial
,)$)-/V)")%$K'%#'%4./-$;"$>'I,%#'0);(#'$/'n&)#$%/"'$,)'+/"+).$'/B'b-).-)#)"$;$%3)'
protected area” in larger marine ecosystem like the Maldives regions atoll complex.
ACKNOWLEDGMENTS
Thanks are expressed to Serge Andréfouët and Shiham Adam who provided
&#'$,)'/../-$&"%$K'$/'#$&(K'B/-'$,)'A-#$'$%4)'$,)'4;+-/;0V;0'U/-;'/B'6;;>'I,)'.-/R)+$'
was supported by the French Fondation pour la Recherche sur la Biodiversité (FRB)
and by the Atoll Ecosystem Conservation project. This work is part of the COREUS
team Programme (Institut de Recherche pour le Développement). Laury Dijoux and
Nathalie Duong are thanked for their contribution to molecular analysis on Halimeda
and Dictyotales. Mélanie Hamel is thanked for her contribution to the various maps
given in this manuscript. The Marine Research Center of the Maldives is acknowledged
B/-'#+%)"$%A+'+/00;E/-;$%/"5';"('<)';-)')#.)+%;00K'$,;"TB&0'$/'D,;AK;':;))4';"('q//#&B'
Rilwan from MRC for their logistic and sampling assistance as well as their hospitality
;"('<;-4%"V'+/4.;"K'(&-%"V'$,)'A)0('#&-3)K>'_)';0#/'$,;"T'$,)':/;,'$);4'B/-',;3%"V'
made our life onboard easy and enjoyable. Finally, our thanks are addressed to Dr Roy
Tsuda for his helpful comments on the manuscript.
Table 4. Species richness, Sorensen’s similary Index (SI =2x/2x+y+z; where x is
the number of shared species, y'$,)'"&4E)-'/B'$,)'$/$;0'#.)+%)#'/B'$,)'A-#$'%#0;"('
and z is the total species of the second island or group) and % of common species
calculated between species diversity in Baa atoll and other archipelagoes of the
West Indian Ocean.
Baa
Maldives
Laccadives
Chagos
Seychelles
Reunion
Rhodophyta
108
200
71
26
212
122
Chlorophyta
58
]^
41
34
102
58
Phaeophyceae
10
24
20
7
54
36
Total species
176
321
132
68
374
215
Shared species
63
45
31
76
52
% Baa
35.7
25.5
17.6
43.1
W].5
Sorensen index
(SI)
0.24
0.22
0.2
0.21
0.21
!
!
44
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Micronesica'NW@'W^]GWPW>
Tsuda, R.T., and J. Newhouse.
N]OO>'' S;-%")'E)"$,%+';0V;)'B-/4'8((&'8$/005'S;0(%3)'!#0;"(#>'..>']YtNXW>'
In D.R. Stoddart (ed.), Reef studies at Addu Atoll, Maldive Islands,
46
7-)0%4%";-K'-)#&0$#'/B';"')M.)(%$%/"'$/'8((&'8$/00'%"'N]O`>'Atoll Research
Bulletin NNO@'NtNWW>
Vroom, P. S. K.N. Page, K.A. Peyton and J. K. Kukea-Shultz
2005. Spatial heterogeneity of benthic community assemblages with an emphasis
on reef algae at French Frigate Shoals, Northwestern Hawai‘ian Islands.
Coral reefs'W`@9^`G9PN'>'
Weber Van Bosse, A., and M. Foslie
N]X`>' 'I,)'=/-;00%";+);)'/B'$,)'D%E/V;'?M.)(%$%/">'D%E/V;'?M.)(%$%)'ON>'?>[>'
Brill, Leyden.
Weber-van Bosse, A.
N]N`>'' I,)'7)-+K'D0;()"'I-&#$'?M.)(%$%/"'$/'$,)'!"(%;"'L+);"'%"'N]X95'&"()-'
$,)'0);()-#,%.'/B'S->'[>'D$;"0)K'\;-(%")-5'S>8>'*)./-$#@':/>'u!Z>'S;-%")'
algae, Rhodophyceae. Transactions of the Linnean Society of London, Sec-
ond Series, Zoology NO@'WO]GYXO>
Wynne M.J.
N]]Y>' '6)"$,%+'4;-%")';0V;)'B-/4'$,)'S;0(%3)#5'!"(%;"'L+);"5'+/00)+$)('(&-%"V'
the RV Te Vega Expedition. Contributions of the University of Michigan
Herbarium N]@'9GYX5'N`>
47
Appendix 1. Taxonomic list of the macrophytes recorded for Baa Atoll during the present study
Rhodophyta
Bonnemaisoniales
Bonnemaisoniaceae
Asparagopsis
taxiformis
(Delile) Trevisan
Ceramiales
Callithamniaceae
Crouania
minutissima
Yamada
Seirospora
orientalis
G. T. Kraft
Ceramiaceae
Centroceras
clavulatum
(C. Agardh) Montagne
Centroceras
minutum
Yamada
Ceramium
maryae
Weber-van Bosse
Ceramium
mazatlanense
E.Y. Dawson
Corallophila
apiculata
(Yamada) R.E. Norris
Cryptonemia
umbraticola
E.Y. Dawson
Gayliella
transversalis
FQ>D>'=/00%"#')$'d)-3)KH'I>L>'=,/')$'Q-)()-%+n
Griffithsia
heteromorpha
Kützing
Dasyaceae
Dasya
anastomosans
(Weber-van Bosse) M.J. Wynne
Dasya
baillouviana
(S. G. Gmelin) Montagne
Dasya
palmatifida
(Weber-van Bosse) A.J.K. Millar et E. Coppejans
Dictyurus
purpurascens
Bory de Saint-Vincent
Heterosiphonia
crispella
(C. Agardh) M.J. Wynne
Thuretia
sp
Delesseriaceae
Hypoglossum
simulans
M.J. Wynne, Price et Ballantine
Martensia
fragilis
Harvey
Martensia
sp. 'petit'
Myriogramme
heterostroma
N'Yeurt, M.J. Wynne et Payri
Myriogramme
melanesiensis
N'Yeurt, M.J. Wynne et Payri
Myriogramme
sp.
Nitophyllum
adhaerens
M. J. Wynne
Rhodomelaceae
Acanthophora
pacifica
(Setchell) Kraft
Chondria
arcuata
Hollenberg
Chondria
bullata
N'Yeurt et Payri
Chondria
ryukyuensis
Yamada
Chondria
simpliciuscula
Weber-van Bosse
Chondrophycus
succisus
(A.B. Cribb) K.W. Nam
Coelothrix
irregularis
(Harvey) Børgesen
Dipterosiphonia
dendritica
(C. Agardh) F. Schmitz
48
Herposiphonia
secunda
(C. Agardh) Ambronn f. tenella (C. Agardh) M.J. Wynne
Rhodophyta
Ceramiales
Rhodomelaceae
Laurencia
cf minuta
Vandermeulen, Garbary et Guiry
Laurencia
distichophylla
J. Agardh
Laurencia
sp. 1
Laurencia
sp. 2
Laurencia
sp. 3
Laurencia
sp. 4
Laurencia
sp. 5
Leveillea
jungermannioides
(K. Hering et G. Martens) Harvey
Neosiphonia
apiculata
(Hollenberg) Masuda et Kogame
Neosiphonia
ferulacea
(Suhr ex J. Agardh) S.M. Guimarães et M.T. Fujii
Palisada
parvipapillata
(C. K. Tseng) K. W. Nam
Polysiphonia
delicatula
Hollenberg
Polysiphonia
sertularioides
(Grateloup) J. Agardh
Tolypiocladia
glomerulata
(C. Agardh) F. Schmitz
Wrangeliaceae
Wrangelia
sp. inedit
Corallinales
Corallinaceae
Amphiroa
foliacea
Lamouroux in Quoy et Gaimard
Amphiroa
fragilissima
(Linnaeus) Lamouroux
Amphiroa
rigida
J.V. Lamouroux
Amphiroa
tribulus
(Ellis et Solander) Lamouroux
Amphiroa
sp
Hydrolithon
gardneri
!"#$%&'()*'+,'&-).)/+012,#33')456)7'&6'
Hydrolithon
onkodes
(Heydrich) D. Penrose et Woelkerling
Hydrolithon
reinboldii
(Weber-van Bosse et Foslie) Foslie
Hydrolithon
sp
Jania
adhaerens
Lamouroux
Lithophyllum
bamleri
(Heydrich) Heydrich
Lithophyllum
kotschyanum
Unger
Lithothamnion
proliferum
Foslie
Lithothamnion
sp
Mesophyllum
erubescens
(Foslie) M. Lemoine
Mesophyllum
sp
Neogoniolithon
brassica-florida
(Harvey) Setchell et L.R. Mason
Neogoniolithon
frutescens
!"#$%&'()8'9:,'%%).);<7<=5$#6
Appendix 1 (Con’td)
`]
Neogoniolithon
laccadivicum
!"#$%&'()*'+,-'%%).)/0$#1
Rhodophyta
Gelidiales
Gelidiaceae
Caulacanthus
ustulatus
(Turner) Kützing
Gelidium
isabelae
W.R. Taylor
Gelidium
sp
Pterocladiella
caespitosa
(Kylin) Santelices
Pterocladiella
caloglossoides
(M.A. Howe) Santelices
Gelidiellaceae
Gelidiella
acerosa
(Forsskål) Feldmann et G. Hamel
Gelidiella
myrioclada
(Børgesen) Feldmann et G. Hamel
Gigartinales
Corynocystaceae
Corynocystis
prostrata
G.T. Kraft
Dumontiaceae
Gibsmithia
dotyi
Kraft et Ricker
Gibsmithia
hawaiiensis
Doty
Hypneaceae
Hypnea
nidulans
Setchell
Hypnea
pannosa
J. Agardh
Hypnea
spinella
(C. Agardh) Kützing
Kallymeniaceae
Kallymenia
thompsonii
Abbott et McDermid
Peyssonneliaceaea
Peyssonnelia
cf. boergesenii
Weber-van Bosse
Peyssonnelia
inamoena
Pilger
Rhizophyllidaceae
Portieria
hornemannii
(Lyngbye) P.C. Silva
Halymeniales
Halymeniaceae
Halymenia
actinophysa
M. A. Howe
Halymenia
durvillei
Bory de Saint-Vincent
Halymenia
maculata
J. Agardh
Nemaliales
Galaxauraceae
Actinotrichia
fragilis
(Forsskål) Børgesen
Actinotrichia
sp
Galaxaura
filamentosa
R. Chou
Rhodymeniales
Champiaceae
Champia
compressa
Harvey
Champia
parvula
(C. Agardh) Harvey
Coelothrix
irregularis
(Harvey) Børgesen
Faucheaceae
Gloiocladia
iyoensis
(Okamura) R. Norris
Leptofaucheaceae
Leptofauchea
sp
Rhodymeniaceae
Asteromenia
anastomosans
(Weber-van Bosse) G. W. Saunders, C. E. Lane, C. W.
Schneider et Kraft
Botryocladia
skottsbergii
(Børgesen) Levring
Botryocladia
tenuissima
W.R. Taylor
Appendix 1 (Con’td)
50
Rhodophyta
Rhodymeniales
Rhodymeniaceae
Chamaebotrys
boergesenii
(Weber-van Bosse) Huisman
Gelidiopsis
intricata
(C. Agardh) Vickers
Halichrysis
irregularis
Kützing
Lomentaria
corallicola
Børgesen
Rhodymenia
sp.1
Rhodymenia
sp.2
Rhodymenia
sp.4
Rhodymenia
sp.5
Spirocladia
barodensis
Børgesen
Sporolithales
Sporolithaceae
Sporolithon
ptychoides
Heydrich
Chlorophyta
Bryopsidales
Bryopsidaceae
Bryopsis
pennata
J.V. Lamouroux
Bryopsis
plumosa
(Hudson) C. Agardh
Bryopsis
sp
Caulerpaceae
Caulerpa
cupressoides
(Vahl) C. Agardh
Caulerpa
diligulata
G.T. Kraft et A.J.K. Millar
Caulerpa
filicoides
Yamada
Caulerpa
nummularia
Harvey ex J. Agardh
Caulerpa
racemosa
(Forsskål) J. Agardh var. peltata (Lamouroux) Eubank
Caulerpa
sedoides
C. Agardh
Caulerpa
serrulata
(Forsskål) J. Agardh
Caulerpa
sertularioides
(S. Gmelin) M. Howe
Caulerpa
taxifolia
(Vahl) C. Agardh
Caulerpa
tongaensis
Papenfuss
Codiaceae
Codium
arabicum
Kützing
Codium
geppiorum
O.C. Schmidt
Halimedaceae
Halimeda
cuneata
Hering
Halimeda
discoidea
Decaisne
Chlorophyta
Bryopsidales
Halimedaceae
Halimeda
distorta
(Yamada) Hillis-Colinvaux
Halimeda
fragilis
W.R. Taylor
Halimeda
gracilis
Harvey ex J. Agardh
Halimeda
micronesica
Yamada
Halimeda
minima
(W.R. Taylor) Colinvaux
Halimeda
opuntia
(Linnaeus) Lamouroux
Halimeda
taenicola
W.R. Taylor
Appendix 1 (Con’td)
51
Chlorophyta
Bryopsidales
Halimedaceae
Halimeda
velasquezii
W.R. Taylor
Halimeda
xishaensis
S>e>1/"V'C'=>r>I#)"V
Halimeda
sp
Udoteaceae
Avrainvillea
lacerata
Harvey ex J. Agardh
Boodleopsis
pusilla
(F.S. Collins) W.R. Taylor, A.B. Joly et Bernatowicz
Boodleopsis
sp.
Chlorodesmis
fastigiata
(C. Agardh) Ducker
Chlorodesmis
hildebrandtii
A. Gepp et E.S. Gepp
Rhipidosiphon
javensis
Montagne
Rhipilia
crassa
A.J.K. Millar et Kraft
Rhipiliella
verticillata
G.T. Kraft
Rhipiliopsis
gracilis
Kraft
Tydemania
expeditionis
Weber-van Bosse
Chlorophyta
Cladophorales
Anadyomenaceae
Anadyomene
wrightii
Harvey ex J. Gray
Cladophora
dotyana
Gilbert
Cladophora
feredayoides
Kraft et Millar
Cladophora
goweri
A.H.S. Lucas
Cladophora
prehendens
Kraft et Millar
Cladophora
rupestris
(Linnaeus) Kützing
Cladophora
vagabunda
(Linnaeus) Hoek
Cladophora
sp.
Microdictyon
okamurae
Setchell
Siphonocladacaeae
Boergesenia
forbesii
(Harvey) J. Feldmann
Boodlea
composita
(Harvey) F. Brand
Cladophoropsis
herpestica
(Montagne) M.A. Howe
Cladophoropsis
vaucheriaeformis
(J.E Areschoug) Papenfuss
Dictyosphaeria
cavernosa
(Forsskål) Børgesen
Dictyosphaeria
versluysii
Weber-van Bosse
Phyllodictyon
anastomosans
(Harvey) Kraft et M.J. Wynne
Valoniaceae
Valonia
aegagropila
C. Agardh
Valonia
fastigiata
Harvey ex J. Agardh
Valonia
ventricosa
J. Agardh
Valoniopsis
pachynema
(G. Martens) Børgesen
Chlorophyta
Dasycladales
Dasycladaceae
Neomeris
annulata
Dickie
Appendix 1 (Con’td)
52
Polyphysaceae
Parvocaulis
parvulus
(Solms-Laubach) S. Berger et al.
Ulvales
Ulvaceae
Ulva
flexuosa
(Wulfen) J. Agardh
Phaeophyceae
Dictyotales
Dictyotaceae
Dictyopteris
repens
(Okamura) Børgesen
Dictyota
bartayresiana
Lamouroux
Phaeophyceae
Dictyotales
Dictyotaceae
Dictyota
ceylanica
Kützing
Dictyota
friabilis
Setchell
Dictyota
grossedentata
De Clerck et Coppejans
Dictyota
humifusa
Hörnig, Schnetter et Coppejans
Dictyota
sp.1
Lobophora
variegata
(Lamouroux) Womersley ex Oliveira
Padina
okinawaensis
Ni-NI-_%"5'D>'8-;%'C'd>'r;<;%
Fucales
Sargassaceae
Turbinaria
ornata
(Turner) J. Agardh
Magnolophyta
Alimastales
Cymodoceacea
Syringodium
isoetifolium
(Ascherson) Dandy
Hydrocharitaceae
Thalassia
hemprichii
(Ehrenberg) Ascherson
!
Appendix 1 (Con’td)
53
Appendix 2. Presence /absence of macroalgal species at prospected sites in Baa Atoll
Genus
species
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
25
27
28
!
!
Anadyomene wrightii
!!
!!
"!
!!
!!
!!
!!
"!
!!
!!
!!
"!
!!
!!
"!
!!
"!
"!
!!
!!
"!
!!
!!
"!
!!
!!
!!
Avrainvillea lacerata
!
!
!
!
!
!
!
!
!
!
"!
!
!
"!
!
!
!
!
"!
!
"!
"!
!
!
"!
!
"!
Boergesenia forbesii
!!
!!
!!
"!
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
"!
Boodlea composita
!
!
!
!
!
!
!
"!
"!
!
"!
!
"!
!
!
"!
!
"!
"!
!
"!
!
!
!
!
!
"!
Boodleopsis pusilla
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
"!
!!
!!
!!
!!
!!
!!
!!
!!
Boodleopsis
#$%!
!
!
"!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
Bryopsis pennata
!!
!!
"!
"!
!!
!!
"!
"!
!!
"!
"!
"!
!!
"!
!!
"!
!!
!!
"!
!!
"!
"!
!!
"!
"!
!!
!!
Bryopsis plumosa
!
!
!
!
!
!
!
!
!
!
!
"!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
Bryopsis
#$%!
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
"!
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
"!
!!
"!
Caulerpa cupressoides
!
!
!
!
!
!
!
!
"!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
Caulerpa diligulata
"!
!!
!!
"!
!!
!!
"!
!!
!!
"!
"!
!!
!!
"!
!!
!!
"!
"!
"!
!!
!!
!!
!!
!!
!!
"!
!!
Caulerpa filicoides
!
!
!
!
!
!
!
!
!
!
!
!
!
"!
!
!
!
!
!
!
!
!
!
!
!
!
!
Caulerpa nummularia
!!
!!
!!
!!
!!
"!
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
"!
"!
!!
!!
Caulerpa racemosa
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
"!
!
"!
Caulerpa sedoides
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
"!
!!
!!
!!
!!
!!
!!
!!
!!
!!
Caulerpa serrulata
!
!
!
!
"!
!
!
!
"!
!
!
!
!
!
!
!
"!
"!
!
!
!
!
!
!
!
!
!
Caulerpa sertularioides
!!
!!
!!
!!
!!
"!
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
Caulerpa taxifolia
!
!
!
!
!
!
!
"!
!
!
!
!
!
!
!
"!
"!
!
!
!
!
!
!
!
!
!
!
Caulerpa tongaensis
!!
!!
!!
!!
!!
!!
!!
!!
!!
"!
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
Chlorodesmis fastigiata
!
!
!
!
!
!
!
!
!
!
"!
!
!
!
!
!
"!
"!
"!
!
!
!
!
!
!
!
!
Chlorodesmis hildebrandtii
"!
!!
!!
!!
!!
!!
!!
"!
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
"!
!!
Cladophora dotyana
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
"!
"!
!
!
!
!
!
!
!
!
!
Cladophora feredayoides
"!
!!
!!
"!
!!
!!
"!
!!
!!
"!
!!
!!
!!
"!
!!
!!
!!
"!
!!
!!
!!
!!
!!
!!
!!
!!
!!
Cladophora goweri
!
!
!
!
!
!
!
!
"!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
Cladophora prehendens
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
"!
!!
!!
!!
!!
!!
"!
!!
!!
!!
!!
!!
Cladophora rupestris
"!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
Cladophora vagabunda
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
"!
!
!
!
Cladophora
#$%!
!!
!!
!!
"!
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
Cladophoropsis herpestica
!!
!!
!!
!!
!!
!!
!!
!!
!!
"!
!!
!!
!!
!!
!!
!!
"!
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
Cladophoropsis vaucheriaeformis
"!
!
!
"!
!
!
"!
!
!
"!
"!
!
!
"!
"!
!
!
"!
"!
!
!
!
!
!
!
"!
!
Codium arabicum
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
!!
"!
54
Codium geppiorum !"
"
"
"
"
"
"
!"
"
"
"
!"
"
"
"
"
"
"
"
"
"
"
"
"
"
"
"
Dictyosphaeria cavernosa "" "" "" "" "" "" "" "" "" "" "" "" "" "" "" "" "" "" "" "" "" "" "" "" !" "" ""
Dictyosphaeria versluysii
"
"
"
"
"
"
"
!"
"
"
"
"
"
"
"
"
"
"
"
"
"
"
"
"
"
"
"
Halimeda cuneata !" "" !" "" !" !" "" "" "" "" "" "" "" !" "" "" !" !" !" "" !" !" "" !" !" !" !"
Halimeda distorta !"
"
"
"
!" !" !"
"
"
"
!"
"
"
!"
"
"
"
"
!"
"
"
"
!"
"
"
!"
"
Halimeda gracilis !" "" "" "" !" !" !" "" "" "" !" "" "" "" "" !" !" !" "" "" !" "" "" !" !" "" !"
Halimeda micronesica
"
"
"
"
"
"
"
"
"
"
"
"
"
"
"
"
"
"
!" !"
"
"
"
"
"
"
"
Halimeda minima "" "" !" "" !" !" !" !" "" !" !" !" "" !" "" !" !" !" !" "" !" !" "" !" !" !" !"
Halimeda opuntia !" !"
"
"
"
!"
"
!" !" !" !" !" !" !" !"
"
"
!" !" !"
"
"
"
"
!"
"
!"
Halimeda taenicola
"
"
"
"
"
"
"
"
"
"
"
"
"
"
"
"
"
"
!" !"
"
"
"
"
"
"
"
Halimeda velasquezii "" "" "" "" "" "" "" "" "" "" "" "" "" !" "" "" "" "" "" "" "" "" "" "" "" "" ""
Halimeda xishaensis
"
"
"
"
"
"
!"
"
"
"
"
"
"
!"
"
"
"
"
"
"
"
"
"
"
"
!"
"
Halimeda #$%" "" "" "" "" !" "" "" "" "" "" "" "" "" "" "" "" "" "" "" "" "" "" "" "" "" "" ""
Microdictyon okamurae "" "" "" "" "" "" "" "" "" "" "" "" "" !" "" "" "" "" "" "" "" "" "" "" "" "" ""
Neomeris annulata
"
"
"
"
"
"
"
!" !"
"
"
"
"
"
"
"
"
"
"
"
"
"
"
"
"
"
"
Parvocaulis parvulus "" "" "" "" "" "" "" "" "" "" "" "" !" "" "" "" "" "" "" "" "" "" "" "" "" "" ""
Phyllodictyon anastomosans
"
"
!"
"
"
"
!"
"
"
"
!"
"
"
!"
"
"
"
!"
"
"
!"
"
"
!"
"
!"
"
Rhipidosiphon javensis "" "" !" !" !" !" "" "" "" "" "" !" "" !" "" "" !" !" !" "" "" !" "" !" !" "" !"
Rhipilia crassa
"
"
"
"
"
"
"
"
"
"
"
"
"
!"
"
"
"
"
"
"
"
"
"
"
"
"
!"
Rhipiliella verticillata "" "" !" "" "" "" "" "" "" "" "" !" "" "" "" "" !" "" "" "" "" "" "" !" "" "" ""
Rhipiliopsis gracilis
"
"
"
"
"
"
"
"
"
"
"
"
"
"
"
"
"
"
"
"
!"
"
"
"
"
"
"
Tydemania expeditionis !" "" !" !" "" !" !" "" "" !" !" !" "" !" !" "" !" !" !" !" !" !" "" !" !" !" !"
Ulva flexuosa
"
"
"
"
"
"
"
"
"
"
"
"
!"
"
"
"
"
"
"
"
"
!"
"
"
"
"
"
Valonia aegagropila "" !" "" "" "" "" "" "" "" "" "" "" "" "" "" "" "" "" "" "" "" "" "" "" "" "" ""
Valonia fastigiata
"
"
"
!"
"
"
"
"
"
"
"
"
"
!"
"
"
"
"
"
"
"
"
"
"
"
"
"
Valonia ventricosa !" "" !" "" !" "" "" "" "" "" "" "" "" !" "" "" "" "" "" "" "" !" "" !" "" "" ""
Valoniopsis pachynema
"
"
"
"
"
"
"
"
"
"
"
"
"
"
"
"
"
"
"
"
!"
"
"
"
"
"
"
Dictyopteris repens "" "" !" "" "" "" "" "" "" "" "" !" "" "" !" "" "" "" "" "" !" "" "" "" !" "" ""
Dictyota bartayresiana
"
"
"
"
"
!" !"
"
"
"
"
"
"
"
"
"
"
"
"
"
"
"
"
"
"
"
"
Dictyota ceylanica "" "" "" "" "" "" "" "" !" "" "" "" "" "" "" "" "" "" "" "" "" "" "" "" "" "" ""
Dictyota friabilis !"
"
"
"
"
!" !" !"
"
!" !"
"
"
"
"
"
!" !" !"
"
!"
"
"
!" !"
"
"
Dictyota grossedentata "" "" "" "" "" "" "" "" "" "" !" "" "" "" "" "" "" "" "" "" "" "" "" "" "" "" ""
Dictyota humifusa
"
"
"
"
"
"
!"
"
"
!" !"
"
"
"
"
"
"
!"
"
"
"
"
"
"
"
"
!"
Dictyota #$%!" "" "" !" "" "" "" "" "" "" "" "" "" "" "" "" "" "" "" "" "" "" "" "" "" "" "" ""
Lobophora variegata !"
"
!"
"
!" !" !"
"
"
!" !" !"
"
"
"
"
"
!"
"
"
!"
"
"
!"
"
"
"
Padina okinawaensis "" "" "" "" "" "" "" "" !" "" "" "" "" "" !" "" "" !" "" "" "" "" "" "" "" "" ""
Appendix 2 (Con’td)
Genus
species
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
25
27
28
55
Turbinaria ornata
!
!
!
!
"! "!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
Acanthophora pacifica !! !! !! !! !! "! "! !! !! "! "! !! !! "! !! "! !! !! !! !! !! !! !! !! !! "! !!
Actinotrichia fragilis
!
!
"!
!
"!
!
!
!
!
!
"! "!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
"!
Actinotrichia #$%! "! !! "! !! !! "! "! !! !! !! "! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !!
Amphiroa foliacea
!
!
"!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
Amphiroa fragilissima !! !! !! !! !! !! !! !! !! !! !! !! !! "! !! !! !! !! !! !! !! !! !! !! !! !! !!
Amphiroa rigida
!
!
"!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
Amphiroa tribulus
!
!
"!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
Amphiroa sp. !! !! !! !! !! !! !! !! !! "! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !!
Asparagopsis taxiformis !! !! !! !! !! !! !! "! !! !! !! !! !! !! "! !! !! !! !! !! !! !! !! !! !! !! !!
Asteromenia anastomosans
!
!
!
"!
!
!
"!
!
!
!
!
!
!
"!
!
!
!
!
!
!
!
!
!
!
!
"!
!
Botryocladia skottsbergii !! !! !! !! !! "! !! !! !! !! "! !! !! !! "! !! !! !! !! !! "! !! !! !! !! "! "!
Botryocladia tenuissima
!
!
"!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
Caulacanthus ustulatus !! !! !! !! !! !! !! !! !! !! !! "! !! !! !! !! !! !! !! !! !! !! !! !! !! !! "!
Centroceras clavulatum
!
!
!
!
!
!
!
!
!
!
!
!
"!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
Centroceras minutum !! !! !! !! !! !! !! !! "! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !!
Ceramium maryae
!
!
"!
!
"!
!
!
!
!
"! "!
!
!
!
!
"!
!
!
!
!
!
!
!
!
!
!
!
Ceramium mazatlanense !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! "! !! !! !! !! !! !! !! !! !! !! !!
Chamaebotrys boergesenii "!
!
!
!
!
!
"!
!
!
!
!
"!
!
!
!
!
!
!
!
!
!
!
!
!
!
"!
!
Champia compressa !! !! "! "! !! "! "! !! !! !! "! !! !! !! !! !! "! !! !! !! !! "! !! "! "! !! "!
Champia parvula
!
!
!
!
!
!
!
!
"!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
"!
!
!
Chondria arcuata !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! "! !! !! !! !! !! !! !! !!
Chondria bullata
!
!
!
!
!
!
!
!
!
!
!
!
!
"!
!
!
!
!
!
!
!
!
!
!
!
!
!
Chondria ryukyuensis !! !! !! !! !! !! !! !! !! "! !! !! !! !! !! !! !! !! "! !! !! !! !! !! !! !! !!
Chondria simpliciuscula
!
!
"!
!
!
!
!
!
"!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
Chondrophycus succisus !! !! !! !! !! !! !! !! !! !! "! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !!
Coelothrix irregularis
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
"!
Corallophila apiculata !! !! !! !! !! "! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !!
Corynocystis prostrata
!
!
!
!
"!
!
!
!
!
!
!
!
!
!
!
!
!
"!
!
!
"!
!
!
!
!
!
!
Crouania minutissima !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! "! !! !! !! !! !! !! !! !! !! !! !!
Cryptonemia umbraticola "!
!
!
!
"!
!
!
!
!
!
!
!
!
"!
!
!
"! "!
!
!
!
!
!
!
!
!
!
Dasya anastomosans !! !! !! !! !! !! "! !! !! !! !! !! !! !! !! !! !! !! !! !! "! !! !! !! !! !! !!
Dasya baillouviana
!
!
!
!
!
!
!
!
!
!
!
!
!
"!
!
!
!
"!
!
!
!
!
!
!
!
!
!
Dasya palmatifida !! !! !! !! !! !! !! "! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !!
Dictyurus purpurascens
!
!
"!
!
!
!
!
"!
!
!
!
!
!
!
!
!
!
!
!
!
"!
!
!
!
!
!
"!
Dipterosiphonia dendritica !! !! !! !! !! !! "! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !!
Appendix 2 (Con’td)
Genus
species
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
25
27
28
56
Leveillea jungermannioides !! !! !! !! !! !! !! !! !! !! "! !! "! !! "! !! !! !! !! !! !! !! !! !! !! !! !!
Lithophyllum bamleri "!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
Lithophyllum kotschyanum "! !! "! !! "! "! !! !! !! !! !! !! !! !! !! "! !! !! !! !! "! "! !! "! "! !! "!
Lithothamnion proliferum "! !! !! "! "! !! "! !! !! "! "! !! !! "! !! !! !! "! !! !! "! "! !! "! "! "! "!
Lithothamnion #$!
!
!
!
"! "!
!
!
!
!
"!
!
!
!
"!
!
!
!
"!
!
!
"! "!
!
"! "! "!
!
Lomentaria corallicola
!
!
!
!
!
!
!
!
!
!
"!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
Martensia fragilis !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! "! !! !! !! !! !! !! "! !!
Martensia #$!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
"!
!
!
!
!
!
!
"!
!
!
Mesophyllum erubescens !! !! !! !! !! !! !! !! !! "! "! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !!
Mesophyllum #$!
!
!
!
"!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
"!
!
!
!
!
!
!
Myriogramme heterostroma !! !! !! !! !! !! "! !! !! !! !! !! !! !! !! !! !! !! !! !! "! !! !! "! !! !! !!
Myriogramme melanesiensis
!
!
!
!
!
!
!
!
!
!
!
!
!
"!
!
!
!
!
!
!
!
!
!
!
!
!
!
Myriogramme #$! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! "! !! !! "! !! !! !!
Neogoniolithon brassica-florida
!
!
!
!
!
!
!
!
"!
!
!
!
"!
!
!
!
!
!
!
!
"! "!
!
!
!
!
!
Neogoniolithon frutescens "! "! !! !! !! !! !! !! !! !! !! !! "! !! !! !! !! !! !! !! "! "! !! !! !! !! !!
Neogoniolithon laccadivicum
!
"!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
"!
!
!
!
!
!
Neosiphonia apiculata !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! "! !! !! !! !! !! !! !! !!
Neosiphonia ferulacea
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
"!
!
!
!
!
!
!
!
!
!
Nitophyllum adhaerens !! !! "! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !!
Palisada
parvipapillata
!
!
!
!
!
!
!
"!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
Peyssonnelia cf. boergesenii !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! "! !! !! !!
Peyssonnelia inamoena
!
!
!
!
!
!
!
!
!
!
!
!
!
"!
!
!
!
!
!
!
!
"!
!
!
!
!
!
Polysiphonia delicatula !! !! !! "! !! !! !! !! !! !! "! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !!
Polysiphonia sertularioides
!
!
!
!
!
"!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
"!
!
!
!
!
!
Portieria hornemannii !! !! !! !! !! !! !! "! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !!
Pterocladiella caespitosa
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
"!
!
Pterocladiella caloglossoides !! !! !! !! "! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !!
Rhodymenia #$%"!
!
!
!
!
!
!
!
!
!
"! "!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
Rhodymenia #$%&! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! "! !! !! !! !!
Rhodymenia #$%'!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
"!
!
Rhodymenia #$%(! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! "!
Seirospora orientalis
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
"!
!
!
!
!
!
!
!
!
!
!
Spirocladia barodensis !! !! !! !! !! !! !! !! !! !! "! !! !! !! !! !! !! "! !! !! !! !! !! !! !! !! !!
Sporolithon ptychoides
!
!
!
"! "! "! "!
!
!
!
"!
!
!
"!
!
!
!
"!
!
!
!
!
!
"!
!
!
"!
Thuretia #$%! !! !! "! "! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !!
Tolypiocladia glomerulata
!
!
!
!
!
!
"!
!
"!
!
!
!
"!
!
!
!
!
!
!
!
!
"!
!
!
!
!
!
Appendix 2 (Con’td)
Genus
species
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
25
27
28
57
Wrangelia sp. inedit !! !! !! !! !! !! !! !! !! !! !! !! !! !! "! !! !! !! !! !! !! !! !! !! "! !! !!
Syringodium isoetifolium !! "! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !!
Thalassia hemprichii !! "! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !! !!
!
Appendix 2 (Con’td)
Genus
species
1
2
3
4
5
6
7
8
9
10
11
12
13
14
15
16
17
18
19
20
21
22
23
24
25
27
28
58
Appendix 3
Rhodophyta 1/4
Gibsmithia hawaiensis!Gibsmithia dotyii!!
Botryocladia skottsbergii Cryptonemia umbraticola
Corynocystis prostrata
Asteromenia anastomosans
!
9]
Rhodophyta 2/4
!
Actinotrichia!"#! Actinotrichia fragilis
!
!
Acanthophora pacifica Amphiroa tribulus
Dictyurus purpurascens!
Kallymenia thompsonii
!
60
Rhodophyta 3/4
Halymenia durvillei
!
Coelothrix irregularis
Gelidium isabelae!Heterosiphonia crispella
Martensia fragilis
!
Myriogramme heterostroma
Myriogramme!"#$!
!
Peyssonnelia "#$!
61
Rhodophyta 3/4
Hydrolithon gardneri
!
Lithothamnion proliferum
!
Hydrolithon "#$!
!
Sporolithon ptychoides.!
62
Chlorophyta 1/4
Caulerpa serrulata!!
Caulerpa racemosa var. peltata
Caulerpa diligulata Tydemania expeditionis
Avrainvillea lacerata!
Rhipidosiphon javensis
!
63
Chlorophyta 2/4
Halimeda cuneata Halimeda distorta
Halimeda gracilis Halimeda micronesica
Halimeda minima
Halimeda opuntia!!
!
!
64
Chlorophyta 3/4
Bryopsis pennata!
Cladophoropsis vaucheriaeformis
Chlorodesmis fastigiata!
Phyllodictyon anastomosans
!!
Cladophora feredayoides!
Microdictyon umbilicatum
!
65
Chlorophyta 4/4
Valonia fastigiata!
Valonia ventricosa!
!
!
!
!
!
!
!
!
!
!
!
!
!
!
Boergesenia forbersii !Boodleopsis pusilla!!
!
!
!
!
!
!
!
66
Phaeophyceae 1/1
Lobophora variegata Padina okinawensis!
Dictyota friabilis
!
Dictyota humifusa
Magnolophyta 1/1
!
Cymodocea serrulata!Syringodium isoetifolium
... In an article published in 1977, Hackett reported the presence and distribution of 205 species. A more recent major survey of benthic algae in the Baa Atoll was conducted by Payri et al. (2012), but molecular analysis of the algae collected was only carried out for samples of Dictyotales (Dictyota, Padina) and Halimeda. While several collections of algae were made during these expeditions to the Maldives, information about the algal diversity of the country still remains sporadic and incomplete. ...
... For example, Dhunya et al. (2017) reported 321 species, the Maldivian Ministry of Environment and Energy (MEE) mentioned 285 algae (21 species of Cyanophyta, 163 Rhodophyta, 83 Chlorophyta, and 18 Phaeophyceae; MEE 2015) and more recently Dryden et al. (2020) indicated the presence of 280 species. All these counts primarily refer to the list provided by the major algal survey conducted by Hackett (1977) and do not account for the more recent study by Payri et al. (2012), nor include additional data from important historical references. Not all algal groups were always considered in previous surveys. ...
... Not all algal groups were always considered in previous surveys. For example, while Payri et al. (2012) brought the total number of species to 321 (200 Rhodophyta, 97 Chlorophyta, and 24 Phaeophyceae), the authors did not include Cyanobacteria. This group of algae, however, was included in previous counts from the Maldives (Hackett 1977;Sigee 1966;Tsuda and Newhouse 1966). ...
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In tropical ecosystems worldwide, benthic marine algae are important primary producers and habitat providers for many juvenile fish and invertebrate species. Calcified species are known to provide structural support to their respective communities, thus enhancing the overall system’s productivity. In the Republic of the Maldives, algae are an important yet currently poorly studied biological resource. We reviewed the literature around algal diversity and distribution across Maldivian atolls and compiled an extensive and updated taxonomic list. The list contains 353 species, of which 31 are Cyanobacteria, 26 Phaeophyceae, 109 Chlorophyta, and 187 Rhodophyta. Algal collections have been reported from 12 out of 20 atolls, and these mostly occurred during 20th century expeditions. The taxonomic status of 110 species has changed since first reported. While several species have been documented from the country, identifications have thus far almost solely relied on morphological assessments. Many of the reported algal groups require molecular confirmation. This suggests that benthic algal diversity from the Maldives is likely an underestimate. Since anthropogenic activities can significantly alter algal community dynamics, a baseline understanding of algal diversity is necessary to determine how such shifts affect the ecosystem as a whole, thus underpinning future management and conservation efforts.
... The Maldives Archipelago is an isolated tropical carbonate platform constituting the central and largest part of the Chagos-Laccadives Ridge, which is located southwest of India (Betzler et al., 2013;Purdy and Bertram, 1993). The archipelago consists of a double row of twenty-six main islands about 1000 km southwest off the Asian continent (Hackett, 1977;Payri et al., 2012). The Maldives islands host tropical communities with affinities with western Indian Ocean (west Africa and Red Sea) and central Indo-Pacific (Indonesia and Australia; e.g., Veron, 1995), although significant differences occur between the African-Red Sea foraminiferal assemblages (Chasens, 1981;Haunold et al., 1997;Heron-Allen and Earland, 1915;Hottinger et al., 1993;Langer et al., 2013;Lévy et al., 1982;Pignatti et al., 2012;Thissen and Langer, 2017) and those of the Indo-Pacific region Goeting et al., 2018Goeting et al., , 2021Goeting et al., , 2022Hofker, 1951;Loeblich Jr. and Tappan, 1994;Parker, 2009;Renema, 2003;Renema and Troelstra, 2001). ...
... In the Maldives, seagrass meadows are located almost exclusively in the intertidal to upper subtidal zones, within a shallow-water lagoon (Milchakova et al., 2005); rarely, they also occur in areas exposed to strong currents, in oceanic-exposed reef flats (Payri et al., 2012). Several observations suggested that seagrasses were more abundant near to the traditional fishing villages than in other areas, where sediments are enriched in anthropogenic phosphorus (Miller and Sluka, 1999). ...
... In most cases, seagrasses form polyspecific associations, with a dominant species. In the investigated areas the following seagrasses are usually recognized: Syringodium isoetifolium (Ascherson) Dandy, Thalassia hemprichii (Ehrenberg) Ascherson, Thalassodendron ciliatum (Forsskal) Hartog ( Green and Short, 2003), Halodule uninervis (Forsskal) Ascherson and Cymodocea rotundata (Ehrenbery and Hemprich ex Ascherson) (Milchakova et al., 2005;Miller and Sluka, 1999;Payri et al., 2012). ...
... The Maldives Archipelago is an isolated tropical carbonate platform constituting the central and largest part of the Chagos-Laccadives Ridge, which is located southwest of India (Betzler et al., 2013;Purdy and Bertram, 1993). The archipelago consists of a double row of twenty-six main islands about 1000 km southwest off the Asian continent (Hackett, 1977;Payri et al., 2012). The Maldives islands host tropical communities with affinities with western Indian Ocean (west Africa and Red Sea) and central Indo-Pacific (Indonesia and Australia; e.g., Veron, 1995), although significant differences occur between the African-Red Sea foraminiferal assemblages (Chasens, 1981;Haunold et al., 1997;Heron-Allen and Earland, 1915;Hottinger et al., 1993;Langer et al., 2013;Lévy et al., 1982;Pignatti et al., 2012;Thissen and Langer, 2017) and those of the Indo-Pacific region Goeting et al., 2018Goeting et al., , 2021Goeting et al., , 2022Hofker, 1951;Loeblich Jr. and Tappan, 1994;Parker, 2009;Renema, 2003;Renema and Troelstra, 2001). ...
... In the Maldives, seagrass meadows are located almost exclusively in the intertidal to upper subtidal zones, within a shallow-water lagoon (Milchakova et al., 2005); rarely, they also occur in areas exposed to strong currents, in oceanic-exposed reef flats (Payri et al., 2012). Several observations suggested that seagrasses were more abundant near to the traditional fishing villages than in other areas, where sediments are enriched in anthropogenic phosphorus (Miller and Sluka, 1999). ...
... In most cases, seagrasses form polyspecific associations, with a dominant species. In the investigated areas the following seagrasses are usually recognized: Syringodium isoetifolium (Ascherson) Dandy, Thalassia hemprichii (Ehrenberg) Ascherson, Thalassodendron ciliatum (Forsskal) Hartog ( Green and Short, 2003), Halodule uninervis (Forsskal) Ascherson and Cymodocea rotundata (Ehrenbery and Hemprich ex Ascherson) (Milchakova et al., 2005;Miller and Sluka, 1999;Payri et al., 2012). ...
... Studies reporting on algal diversity in the Maldives are extremely scarce and tend to be based on taxonomy inventories and species richness analysis, either with no molecular validation of the identified species or with molecular validation carried out only for a few selected specimens (e.g. Dictyota J.V. Lamouroux, Padina Adanson and Halimeda J.V. Lamouroux, from Payri et al. 2012). In reports by the Maldivian government, algae are often broadly described as 'algal turf' (e.g. ...
... However, in this survey, the author only briefly reported on a few species of algae associated with the mangrove Rhizophora mucronata. Although Payri et al. (2012) provided the most comprehensive census of algal diversity in the Maldives to date (321 species), these observations are limited to the Baa Atoll, and there is no mention of the types of habitats these species were associated with. Although very little is known about mangrove-associated macroalgae in the Maldives, mangrove habitats are globally known to support diverse macroalgal communities (Post 1936). ...
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Mangrove forests are one of the most important biological, ecological and economic ecosystems in the world. In the Maldives, they play a crucial role in maintaining coastal biodiversity, providing ecosystem services, such as coastal protection, and supporting livelihoods by providing income and food. Overall, 23 Maldivian islands have at least 1 protected mangrove area. However, knowledge of the mangroves of the Maldives is scarce, scattered and sometimes conflicting. There is a lack of information on a national scale regarding their distribution, diversity, ecological importance and associated biodiversity. The aim of this review is to analyse scientific publications, reports, and online documents on mangroves for the entire Maldivian archipelago to provide the first comprehensive summary of the current state of knowledge of mangroves from a national perspective. This includes the geographical location of mangrove forests, the identity and distribution of mangrove species, ecosystem services, ecological importance and diversity of mangrove-associated flora and fauna. We analysed available information from both the grey literature and scientific publications and found that 14 mangrove species have been documented on 108 islands (9% of all Maldivian islands). Mangroves are mainly concentrated in northern atolls and are associated with diverse flora and fauna. Furthermore, we identified inconsistencies and gaps in the literature and proposed future directions for research. This is crucial for informed decision-making, developing effective conservation strategies and long-term sustainability of mangrove ecosystems.
... The gap of knowledge for marine flora in the Maldives are wide. A survey was undertaken in 2012 to provide a census of the macroalgae and seagrasses of Baa Atoll of the Maldives (Payri, N'Yeurt, & Mattio, 2012). In 2003 digital numbers of seagrasses of rim reefs in the Maldives was geomorphologically analyzed in four spectral bands of the Landsat 7 ETM+ sensor (Naseer, 2003). ...
... Thalassia hemprechii, Syringodium isoetifolium (Payri, et al., 2012) and Thalassodendron ciliatum (Miller & Sluka, 1999). ...
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In this study, the changes of the seagrass beds near L. Maavah from the year 2000 to 2018 was analyzed using remote sensing techniques. The changes were studied using Landsat-7 ETM+ and Lansat-8 OLI images with a spatial resolution of 30m and a ground resolution of 15m for the panchromatic bands. Due to the gap of knowledge for seagrasses in the Maldives it was important to conduct this research to predict the presence or absence of seagrasses and to account environmental impacts. L. Maavah is a fishing village for more than a century and Miller & Sluka (1999) declared that the lagoon was covered in thick seagrasses. The run-offs and organic wastes to the sea increase the seagrass cover (Agardy, et al., 2017). QGIS application was used to mask the cloud cover. The Semi-automatic classification plugin (SCP) in QGIS was used to produce classification of macroclasses. In 2000 the seagrass cover was 7.802% of the study area with an area of 0.892km2. In 2018 the seagrass meadows was more significant with an area of 1.479km2 and cover 12.896% of the study area. This change occur due to the nutrient enrichment of the area from natural phenomenons and anthropogenic activities (Miller & Sluka, 1999). There were no field-transects in the study area for the validity of this research. However, Google Earth processed images were used for the ground truth.
... Biological diversity within the marine environment of Maldives are abundantly rich and outstandingly colorful. It has been documented that there are 258 species of hermatypic corals, 36 species of sponges [11], 321 species of algae [12], 5 species of seagrasses [10], and 80 species of echinoderms in the coral reefs [10]), making the coral reefs of the Maldives one of the most diverse marine ecosystems of the world [10]. ...
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Coastal environments has been always considered as one of the significant source of natural resources for the mankind. However there is growing threats on these extremely fragile, yet richest ecosystems. Anthropogenic presence, pressures along with natural as well as climate change effects had adversely affected the well being of marine ecosystems, impairing structures, functions of theses environments and compromising resource gain from marine and coastal environments. This paper would aim in describing a synopsis of the unique physical and ecological attributes of coastal ecosystem of the Maldives and analyse the main anthropogenic pressures as well as the climate related issues to these ecosystems. Coastal ecosystems of the Maldives are at risk from numerous threats with a range of impact scales from local to global level. Some of the acute stressors are those from climate variability and climate change as well as due to some unregulated fishing practices. Also, chronic stressors like coastal modifications, pollution and economic activities are serious threats to the coastal habitats of the Maldives. There are plentiful of researches available for the coral reefs of Maldives, especially with regard to the bleaching events in the late 90s. However, for the mangroves, sea grasses ecosystems only a handful of studies are available. The main threats to these ecosystems are related to human settlements, infrastructure development resulting from the increasing population. In this paper we highlight the current government strategies for conservation of the habitats and also recommend some applicable ecosystem based management and conservation strategies that are practiced in other parts of the world.
... obs.). However, to date there has been little effort to survey and assess the composition and extent of the seagrass habitat (Milchakova et al., 2005;Payri, N'Yeurt, & Mattio, 2012;Short, Carruthers, Dennison, & Waycott, 2007). Therefore, as island development continues to expand throughout the country, new seagrass habitat is likely to be found, and new species recorded. ...
... L'isolement, la jeunesse des îles et leur histoire géologique (Brousse et al., 1978 ; Cabioch et al., 2008) dans un contexte océanique particulier (Martinez et Maamaatuaiahutapu, 2004 ) se traduisent , entre autres, par une diversité d'habitats réduite. Payri et al., 2012 ) et d'autres groupes biologiques Figure 5– Distribution des espèces par genre dans les neuf îles étudiées, et répartition spatiale de la richesse spécifique entre les groupes du nord, du centre et du sud. me les mollusques (Bouchet et al., 2002). ...
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La flore marine des îles Marquises comptait, jusqu'à l'expédition Pakaihi i te Moana 2011, une dizaine d'espèces connues. Depuis cette date, 144 espèces (à l'exclusion des Corallinales et des Peysson-nelia*) ont été identifiées dans les neuf îles étudiées. Parmi ces espèces on compte 94 Rhodophyta (algues rouges), 38 espèces de Chlorophyta (algues vertes) et 12 Phaeophyceae (algues brunes) avec plusieurs espèces nouvelles pour la science. La végétation est largement dominée par les encroû-tements calcaires d'algues rouges, depuis la surface jusqu'à 40 m de profondeur, en raison du fort hydrodynamisme qui règne tout autour des îles. Les grands types d'habitats observés sont essen-tiellement les plaines sédimentaires, les éboulis, les habitats coralliens dominés par les Porites et les Millepora, les tombants nus et escarpements, et enfin les algueraies. Ces dernières sont dominées par plusieurs espèces d'Halimeda* dont principalement H. distorta, H. melanesica, H. heteromorpha et H. discoidea. La richesse en espèces varie à l'intérieur de l'archipel et d'une île à l'autre, avec un nombre d'espèces plus important dans les îles du centre et du sud de l'archipel. La moitié des espèces n'a été observée que dans une île, et seulement 16 % des espèces ont été vues dans quatre ou plus des neuf îles visitées. Les îles de Ua Huka et de Nuku Hiva montrent la plus grande diversité, en raison notamment d'un plus grand nombre d'habitats dont les cuvettes et failles des trottoirs basaltiques. C'est dans ces habitats, particulièrement riches et diversifiés en algues, que les Marquisiens cueillent encore de nos jours diverses espèces pour leur consommation. Les îles Marquises se distinguent par bien des aspects du reste de la Polynésie française et montrent des affinités biogéographiques avec les îles Hawaii mais aussi avec le Pacifique Est (îles Guadelupe, Revillagigedo et Galápagos). Les caractéristiques naturelles et écologiques de la flore marine, accompagnées de pratiques culturelles encore bien vivantes, confèrent à cet archipel une place singulière dans la société polynésienne. Ces caractéristiques originales contribuent à soutenir un programme régional de conservation.
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Globally, climatic and anthropogenic forcings are causing the catastrophic decline of coral reef ecosystems, which sustain a plethora of marine life and support the livelihoods of several millions of people. Lakshadweep- Maldives-Chagos archipelago (LMC) forms one of the largest chains of atoll systems in the world, and due to remoteness from the mainland, its islands boast a unique set of flora and fauna. The coral reefs of these tropical islands are highly vulnerable to stressors such as climate change, overfishing, monsoon runoff, and ocean acidification. To understand and manage these sensitive ecosystems, knowledge about the existing coral cover and distribution patterns are essential. In the present study, habitat modelling of the two corals Acropora muricata (Linnaeus, 1758) and Porites lutea (Milne Edwards & Haime, 1851) were carried out using the Maximum Entropy (MaxEnt) model to predict the probability of occurrence using remotely sensed environmental variables as predictors. The average test AUC values of 0.980 and 0.974, respectively, for A. muricata and P. lutea as estimated by MaxEnt shows that the model performance for both the species is outstanding. The average uncertainty (standard deviation) was about 0.012 and 0.021 respectively. It is found that the bathymetry is the variable having the highest contribution followed by Calcite and Phosphate for the distribution of both the species. The results of this study throw light on the probable occurrence of coral reefs in many of the hitherto unknown areas, especially the submerged banks and seamounts in the region. Much of these areas are less explored and have strategic positional advantages in increasing the ecosystem connectivity of the region. Furthermore, the relationship between coral distribution and the environmental variables as predicted by this study will be valuable in future conservation activities and designing marine protected areas.
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The understanding of macroalgae functions and processes requires a good understanding of the spatial distribution of the functional diversity of macroalgae. In coral reef environments, this information remains fragmentary. Here, based on 314 species sorted according to a set of 10 functional traits, the functional niches of macroalgae at three remote coral reefs of the Îles Éparses in the Indian Ocean (Europa, Glorioso, and Juan de Nova) are described. For the comparison of intra- and inter-reef functional structures, we characterized both taxonomic and functional beta diversities, and their turnover and nestedness-resultant components. Within the three reefs, we observed strong taxonomic and functional dissimilarities across sampling sites, mainly determined by turnover. Null models highlighted several processes, which structured macroalgal assemblages across sites: a combined effect of environmental variables (geomorphology and wave exposure), limiting similarity and stochastic effects. At the inter-reef scale, the three reefs only shared a small number of species, but the functional beta diversity between Glorioso and Juan de Nova was weak. This suggested that although assemblages were different, fairly similar environmental conditions may have homogenized macroalgae functions through both ecological and evolutionary scale processes. Our results support the idea that macroalgal assemblages can provide similar functional trait portfolios, despite distinct species composition. We stress the need to focus on macroalgae life-history traits for a better understanding of the processes structuring their communities.
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Reefs in tropical atoll systems have historically been described on a geomorphic basis, and segregated into loosely defined fore-reef, back-reef, and lagoonal reef zones. However, recent oceanographic monitoring data have shown that physical factors within a single geomorphic zone can vary significantly, calling into question whether benthic communities within a single zone are biologically similar. To determine the amount of benthic variability that may occur in a geomorphic zone, percent cover of benthic organisms was determined at the species level for 28 sites in three geomorphic zones at French Frigate Shoals, Northwestern Hawai‘ian Islands. Multivariate statistical analyses found most windward fore-reef and back-reef sites to be statistically similar, but considerable variation to exist among sites within calmer lagoonal areas. Surveys revealed macroalgae to dominate over scleractinian coral species at the majority of sites in this healthy, subtropical reef system, although select lagoonal areas were dominated by dense coral communities.
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Sleeping functional group drives coral-reef recovery Current Biology ???? ?????????? Assessing the magnitude of species richness in tropical marine ?????????????????????????????????????????????????????????????? Caledonia site Society????????????? Doty
  • D R Bellwood
  • T P Hughes
  • A S Bouchet
  • P Lozouet
  • P Maestrati
  • V Heros
Bellwood, D.R., T.P. Hughes, and A.S. Hoey 2006. Sleeping functional group drives coral-reef recovery. Current Biology ???? ?????????? Bouchet, P., P. Lozouet, P. Maestrati, and V. Heros 2002. Assessing the magnitude of species richness in tropical marine ?????????????????????????????????????????????????????????????? Caledonia site. Biological Journal of the Linnean Society????????????? Doty, M. S