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Species composition, abundance and distribution of seagrasses in the brackish waters of Balingoan, Misamis Oriental in relation to environmental parameters

Author: Maria Luisa S., Orbita
Publisher: Zenodo
DOI: 10.12692/ijb/16.6.80-89
Source: https://zenodo.org/records/17707839/files/IJB-V16-No6-p80-89.pdf
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Hamisain e al.
In . J. Biosci.
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RESEARCH PAPER OPEN ACCESS
Species composi ion, abundance and dis ibu ion o seag asses
in he b ackish wa e s o Balingoan, Misamis O ien al in
ela ion o en i onmen al pa ame e s
Rodzia D. Hamisain1, Yasmeen A. Sama1, Ma ia Lou des Do o hy G. Lacuna1,
Ronaldo R. O bi a2, Ma ia Luisa S. O bi a1*
1Depa men o Ma ine Science, Mindanao S a e Uni e si y - Iligan Ins i u e o Technology (MSU-
IIT), Iligan Ci y, Philippines
2Depa men o P o essional Educa ion, Mindanao S a e Uni e si y - Iligan Ins i u e o Technology
(MSU-IIT), Iligan Ci y, Philippines
Key wo ds: Seag ass, b ackish wa e , Gingoog Bay.
h p://dx.doi.o g/10.12692/ijb/16.6.80-89
A icle published on June 16, 2020
Abs ac
Seag asses play an impo an ole in ma ine and b ackish wa e s bo h as p ima y p oduce s and ecosys em
enginee s, hus sus aining biodi e si y and ecosys em se ices. The ecology o seag ass was widely in es iga ed
in he ma ine egion whe eas hei abundance and dis ibu ion in b ackish wa e s is s ill limi ed. This s udy
aimed o assess he composi ion, abundance and dis ibu ion o seag asses in ela ion o some en i onmen al
pa ame e s. Field sampling was conduc ed h ough ansec -quad a me hod and shoo densi y was de e mined
along wi h wa e empe a u e, salini y, nu ien s and wa e low. The seag ass bed in Balingoan was a mixed
communi y o H. pini olia, T. hemp ichii, C. o unda a, H. o alis and E. aco oides. H. pini olia domina ed he
a ea and i s dis ibu ion ex ends om high o he lowes in e idal zone. Co ela ion analysis was signi ican
be ween he seag ass species and he en i onmen al pa ame e s and i was species speci ic.
* Co esponding Au ho : Ma ia Luisa S. O bi a  ma ialuisa.o bi [email protected] .edu.ph
In e na ional Jou nal o Biosciences | IJB |
ISSN: 2220-6655 (P in ), 2222-5234 (Online)
h p://www.innspub.ne
Vol. 16, No. 6, p. 80-89, 2020
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2020
In oduc ion
Seag asses a e hizoma ous ma ine angiospe ms
widesp ead in bo h ma ine and b ackish shallow
wa e s om empe a e o opical egions (Sho e
al., 2007). In hese egions, hey o en ac as
ecological enginee s (W igh and Jones, 2006)
o ming ex ensi e meadows ha a e among he mos
p oduc i e ecosys ems on ea h (McRoy and
McMillan, 1997; Dua e and Chiscano, 1999).
Seag ass meadows p o ide key ecosys em se ices,
including o ganic ca bon p oduc ion and expo ,
nu ien cycling, sedimen s abiliza ion, biodi e si y,
and ophic ans e s o adjacen habi a s (Dua e e
al., 2005; Du y, 2006; O h e al., 2006; Cullen-
Unswo h and Unswo h, 2013; Ma co-Mendez e al.,
2015). The abundance and dis ibu ion o seag asses
a e con olled by he physical, chemical and biological
p ope ies o hei en i onmen (G e e and Binze ,
2004). In mos opical seas, which a e usually
cha ac e ized by clea wa e s and high incoming
i adiance h oughou he yea , seag ass g ow h is
o en limi ed by he a ailabili y o nu ien s (Powell e
al., 1989; Sho e al., 1990; Dua e, 1995). In
addi ion, wa e empe a u e, salini y and wa e
mo ion a e also impo an a iables a ec ing seag ass
abundance and dis ibu ion in opical egions (Lin
and Shao, 1998; E emeije and He man, 1994). The
ecology o seag ass was widely in es iga ed in he
ma ine domain whe eas hei abundance and
dis ibu ion in b ackish wa e s is s ill no exhaus i e
(Boscu i e al., 2015). Balingoan is a coas al
municipali y in he p o ince o Misamis O ien al and
i s coas al wa e is pa o he Gingoog Bay. The
coas al a ea has unde wa e sp ing which causes he
wa e o be less saline o b ackish. This unique,
unusual na u al phenomenon p o ides iable
pla o m o scien i ic explo a ion in he a ea because
despi e o i s low salini y, he a ea encompasses a
a ie y o opical habi a s including seag asses. This
s udy aimed o assess he abundance and dis ibu ion
o seag asses in ela ion o some en i onmen al
pa ame e s in he a ea. This s udy p o ides addi ional
da a on he ecology o seag asses and i s ophic ole
in b ackish wa e s especially in he opical egion.
Ma e ials and me hods
S udy a ea
The s udy was conduc ed in Ba angay Man angale,
Balingoan, Misamis O ien al (9°00'26.6''N
124°51'34.4''E, Figu e 1).
Fig. 1. Loca ion o he sampling si e in Balingoan, Misamis O ien al (Sou ces: QGIS e sion 3).
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Hamisain e al.
In . J. Biosci.
2020
The coas al a ea o Man angale in Balingoan has an
unde wa e sp ing ha caused he wa e o be less
saline o b ackish. I had a salini y ha anged om
4-9‰ wi h a mean alue o 6‰. The sampling si e is
known o encompass a a ie y o opical habi a s
including mang o es, seag ass beds and co al ee s.
Field sampling
The s udy was ca ied ou du ing low ide when
seag asses we e exposed. The whole in e idal la was
di ided in o h ee egions: high, middle and low. Fo
each egion, a 50-me e ansec line (wi h 3
eplica es) was placed pa allel o he sho e, and o
e e y 10 m-in e al, a 0.5 m x 0.5 m quad a was laid
down a he igh side o he ansec line. All he
seag asses inside he quad a we e iden i ied and
eco ded ollowing he axonomic keys o Calumpong
and Meñez (1997) and Kuo and den Ha og (2001).
Shoo densi y was measu ed by ca e ully coun ing he
shoo s pe species o each quad a and he shoo
numbe s we e exp essed as densi y (shoo /m-2). The
densi y and ela i e densi y we e calcula ed using he
o mula:
En i onmen al Pa ame e s
En i onmen al pa ame e s we e measu ed andomly
in he b ackish wa e s su ounding he seag ass bed.
Wa e empe a u e was measu ed in si u using an
o dina y me cu y he mome e while salini y was
measu ed using a handheld e ac ome e . Wa e low
was es ima ed using clod ca ds (Do y, 1971) and he
calcula ion o wa e low (cm-2) was done based on
he me hod o Anzai (2001). Nu ien analysis was
ca ied ou ollowing he me hod o G assho e al.
(1983).
S a is ical analysis
The di e ence in abundance ep esen ed by shoo
densi y among species was analyzed h ough One-
Way Analysis o Va iance (One-Way ANOVA, le el o
signi icance, P o 0.05) in SPSS ( e sion 8.0).
Pea son’s co ela ion analysis was used o de e mine
he co ela ion coe icien s be ween en i onmen al
ac o s wi h seag ass abundance.
Resul s and discussion
A o al o i e (5) seag ass species we e iden i ied in
he a ea: Cymodocea o unda a (Eh enbe g and
Hemp ich, ex Asche son), Enhalus aco oides (L. .)
Royle, Halophila o alis (R. B own), Halodule
pini olia (Miki) den Ha og and Thalassia hemp ichii
(Eh enbe g) Asche son (Table 1).
Table 1. Iden i ica ion o seag asses in Balingoan, Misamis O ien al (Calumpong and Meñez, 1997; Kuo and den
Ha og, 2011).
Family
Genus and Species
Common Name
Local Name
Hyd ocha i aceae
Thalassia hemp ichii
Halophila o alis
Enhalus aco oides
Sickle-g ass
Paddle weed
Tape-g ass
Lusay
Lusay
Lusay
Cymodoceaceae
Cymodocea o unda a
Halodule pini olia
Mana ee-g ass
Needle-g ass
Lusay
Lusay
The o al seag ass axa o Balingoan ep esen 33.33%
o he 15 epo ed axa om he Philippines (Meñez e
al., 1983; Sho and Coles, 2001; G een and Sho ,
2003; Sho e al., 2007). The i e (5) seag ass species
in his s udy a e in e es ing in o ma ion conside ing
he o al o i een (15) species o he en i e
Philippines. The seag ass bed o Man angale,
Balingoan was cha ac e ized as mixed meadow and
he seag asses ha o m his mixed bed encompass a
conside able size ange, om he smalles (Halophila
o alis) o he la ges (Enhalus aco oides). Acco ding
o he ollowing au ho s (B ouns, 1987; Fo es, 1995;
Te ados e al., 1998) mos o he seag ass bed in SE
is composed o mixed seag ass communi ies ypically
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2020
comp ise o up o 13 species, anging b oadly in size
om small Halophila sp. o he la ge Enhalus
aco oides. Likewise, Philippine seag ass beds a e
gene ally mixed (Meñez e al., 1983; Tomasko e al.,
1993) in esponse o nu ien en ichmen (Agawin e
al., 1996), dis u bance (Dua e e al., 1997),
compe i ion (Dua e, 2000) and wa e dep h (Taplin
e al., 2005).
Table 2. Co ela ion coe icien s (R) in ela i e densi y (%) wi h en i onmen al pa ame e s among seag ass
species in Balingoan, Misamis O ien al.
Species
Coe icien o Co ela ions
Temp
Sal
PO4
NO3
Wa e low
H. pini olia
-0.147
0.69
-0.748**
0.03
0.510
0.13
0.097
0.79
0.305
0.91
C. o unda a
-0.073
0.83
-0.310
0.35
0.689**
0.02
0.307
0.16
0.075
0.21
H. o alis
-0.007
0.98
-0.693
0.51
0.234
0.15
0.052
0.97
0.725
0.48
T. hemp ichii
-0.999**
0.03
-0.284
0.37
0.303
0.14
0.374
0.23
0.207
0.52
E. aco oides
-0.629
0.26
-0.029
0.94
0.433
0.27
0.500
0.39
0.843**
0.02
Legend: ** ep esen s signi ican di e ences a p<0.05.
The abundance o seag ass ep esen ed by shoo
densi y a ies among species (One-Way ANOVA, p <
0.05). H. pini olia had he highes shoo densi y
ollowed by C. o unda a and T. hemp ichii (Figu e
2). H. pini olia is widely dis ibu ed h oughou he
Indo-wes Paci ic and is almos ubiqui ous in opical
seag ass meadows o en being dominan (Meñez e
al., 1983; Wayco e al., 2004).
This species is a apid colonize om seed and
h ough ege a i e g ow h; i plays an impo an ole
in main aining seag ass habi a in a eas o high
dis u bance and ac i ely s abilizes sedimen s wi h an
in e wining ma o hizomes and ib ous oo s.
Likewise, his species was also dominan in he
coas al lagoon o he eas coas o Malaysia (Sidik e
al., 2010), Valachchenai lagoon (Udageda a e al.,
2017) and Negombo lagoon in S i Lanka
(Sama akoon and Van Zon, 1991). C. o unda a was
second in ank in e ms o abundance. This species is
also an ecologically impo an opical pionee
seag ass species dis ibu ed in he Indo-Paci ic
egion. I is also ound in Pu alam lagoon in S i
Lanka (Ranahewa e al., 2018) and one o he
dominan seag ass species in Tongsha island in
Taiwan (Lin e al., 2005). T. hemp ichii was hi d in
abundance and i is also one o he mos widely
dis ibu ed seag ass species domina ing in many
mixed meadows (den Ha og, 1970; B ouns, 1987;
Ve maa e al., 1995; Gulls öm e al., 2002; P a hep,
2003). This species is known o be an impo an ood
sou ce o dugongs and sea u les and p o ides
c i ical g azing habi a o ish (Phillips and Meñez,
1988). Two species, H. o alis and E. aco oides ha e
he lowes abundance. Halophila plan s in mixed
popula ions ha e low abundance due o high
compe i ion wi h o he species in e ms o ligh , space
and nu ien s (Japa Sidik, 2010). Mo eo e , he low
abundance o E. aco oides was a ibu ed o i s slow
g ow h a e because la ge seag asses a e slow g owing
wi h limi ed colonizing capaci y (Dua e, 1991).
Compa ed o o he opical seag ass species, E.
aco oides is a e y ecognizable ype o seag ass o i
has long, wide and s i lea es (Kuo and den Ha og,
2001) and known o ha e he wides ole ance and
can li e on muddy, sandy and sandy-muddy subs a e
(Dewi and Sukanda , 2017).
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Hamisain e al.
In . J. Biosci.
2020
Fig. 2. The shoo densi y o seag asses in Balingoan, Misamis O ien al. Di e en le e s compa ed ho izon ally
indica e s a is ically signi ican di e ences be ween he means a he le el o 5% p obabili y by Tukey es .
The seag ass communi y was ound 150 me e s om
he sho eline in a dep h o 3 me e s du ing high ide.
The seag asses we e in pa chy dis ibu ion and
ex ends om high o he lowes in e idal zone bu i s
species composi ion dec eases which migh be ela ed
o wa e dep h and ligh a ailabili y (Dua e, 1991).
The i e species we e p esen in he high in e idal
egion and domina ed by H. pini olia wi h 66%
ela i e densi y (Figu e 3). In mid egion, all species
we e s ill p esen and C. o unda a domina ed wi h
59% ela i e densi y. In he low in e idal egion, only
h ee species we e ound such as H. pini olia, C.
o unda a and T. hemp ichii. H. pini olia had he
highes ela i e densi y (57%) ollowed by C.
o unda a (38%).
Fig. 3. The dis ibu ion o seag asses in he in e idal la o Balingoan, Misamis O ien al.

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Signi ican co ela ion was de ec ed in H. pini olia, T.
hemp ichii, C. o unda a and E. aco oides wi h he
en i onmen al pa ame e s measu ed in he a ea
(Pea son’s Co ela ion, p<0.05, Table 2). Wa e
empe a u e showed a signi ican nega i e co ela ion
wi h T. hemp ichii while H. pini olia nega i ely
co ela ed wi h salini y indica ing ha hese species
ha e low capabili y o p oduce high shoo densi y
wi h changing empe a u e and salini y. Tempe a u e
is conside ed a majo ac o con olling seag ass
g ow h because an inc ease in wa e empe a u e will
a ec he biochemical p ocesses in ol ed in
pho osyn hesis and espi a ion (Tu in, 1942; Phillips
e al., 1983; Lee and Dun on, 1996; Lee e al., 2005).
Rela ed s udy shows ha high empe a u es can
educe g ow h and p oduc i i y o T. es udinum
(Ba be and Beh ens, 1985). Likewise, an inc ease in
salini y would a ec he mo phology and physiology
o seag asses (Kuo and den Ha og, 2006; Taiz and
Zeige , 2009). A s udy done on H. w igh ii shows ha
no inc ease in g ow h was seen and he lea
chlo oplas was a ec ed when he plan was exposed
o salini y o 45pp (Fe ei a e al., 2017). On he
o he hand, phospha e was posi i ely co ela ed wi h
C. o unda a sugges ing ha an inc ease in
phospha e would s imula e g ow h o his species,
hence inc eases i s shoo densi y and ice e sa.
Nu ien en ichmen s udies sugges ha addi ions o
ino ganic nu ien s can s imula e seag ass g ow h
(O h, 1977; Ha lin and Tho ne-Mille , 1981; Iizumi
e al., 1982; Dennison e al., 1987; Sho e al., 1990;
Pé ez e al., 1991; Mu ay e al., 1992; Williams and
Ruckelshaus, 1993; Lee and Dun on, 2000) and his
was obse ed in an expe imen done on C. o unda a
in Cape Bolinao, Pangasinan in esponse o nu ien
addi ion (Agawin e al., 1996). Mo eo e , wa e low
was posi i ely co ela ed wi h E. aco oides because
s ong wa e mo ion could inc ease he abso p ion o
ca bon dioxide and inc ease he nu ien up ake a
he lea su ace o E. aco oides (Agawin e al., 2001;
Hillman, 1989).
Conclusion
The ecen esea ch on seag asses in he b ackish
wa e s o Balingoan has p o ided addi ional and
impo an in o ma ion on he composi ion,
abundance and dis ibu ion o seag asses in which
da a we e s ill limi ed. Cu en indings sugges ha
he seag ass bed in Balingoan was a mixed s ands
comp ised p ima ily o H. pini olia, C. o unda a, T.
hemp ichii, H. o alis and E. aco oides. I was
domina ed by H. pini olia and i s dis ibu ion ex ends
om high o he lowes in e idal zone. Seag ass beds
consis ing o H. pini olia con ibu ed impo an ly o
coas al ecosys ems in Balingoan b ackish wa e s
because o i s high densi y. Fu he mo e, he
signi ican co ela ion be ween seag asses and he
en i onmen al pa ame e s in he a ea indica e he
exis ence o a species speci ic ela ionship.
Acknowledgmen
We would like o hank he Depa men o Ma ine
Science, College o Science and Ma hema ics, MSU
- Iligan Ins i u e o Technology o all he suppo
in he conduc o his esea ch.
Re e ences
Agawin NSR, Dua e CM, Fo es MD. 1996.
Nu ien limi a ion o Philippine seag asses (Cape
Bolinao, NW Philippines): in si u expe imen al
e idence. Ma ine Ecology P og ess Se ies 138, 233-
243.
h ps://doi.o g/10.3354/meps138233
Agawin NSR, Dua e CM, Fo es MD, U i JS,
Ve maa JE. 2001. Tempo al changes in he
abundance, lea g ow h and pho osyn hesis o h ee
co-occu ing Philippine seag asses. Jou nal o
Expe imen al Ma ine Biology and Ecology 260(2),
217-239.
h ps://doi.o g/10.1016/s0022-0981(01)00253-2
Anzai R. 2001. The e ec s o co al mo phology and
wa e - low a es on a es o co al g ow h and passi e
di usion. Mas e al Thesis, Uni e si y o he Ryukyus,
Japan.
Ba be BJ, Beh ens PJ. 1985. E ec s o ele a ed
empe a u e on seasonal in si u lea p oduc i i y o
Thalassia es udinum Banks ex König and
86
Hamisain e al.
In . J. Biosci.
2020
Sy ingodium ili o me Kű zing. Aqua ic Bo any 22,
61-69.
h ps://doi.o g/10.1016/0304-3770(85)90029-4
Boscu F, Ma co in I, Sigu a M, B essan E,
Tambe lich F, Vianello A, Casolo V. 2015.
Dis ibu ion modeling o seag asses in b ackish
wa e s o G ado-Mo ano lagoon (No he n Ad ia ic
Sea). Es ua ine, Coas al and Shel Science 164, 183-
193.
h ps://doi.o g/10.1016/j.ecss.2015.07.035
B ouns JJWM. 1987. Aspec s o p oduc ion and
biomass o ou seag ass species (Cymodoceoideae)
om Papua New Guinea. Aqua ic Bo any 27, 333-
362.
h ps://doi.o g/10.1016/0304-3770(87)90073-8
Calumpong HP, Meñez EG. 1997. Field Guide o
he Common Mang o es, Seag asses and Algae o he
Philippines. Bookma k, Inc. Maka i Ci y.
h ps://doi.o g/10.2307/1224050
Cullen-Unswo h L, Unswo h R. 2013. Seag ass
meadows, ecosys em se ices and sus ainabili y.
En i onmen Science and Policy o Sus ainable
De elopmen 55, 14-28.
h ps://doi.o g/10.1080/00139157.2013.785864
Den Ha og C. 1970. The sea-g asses o he wo ld.
No h-Holland Publishing Company, Ams e dam, p.
275p
Dennison WC. 1987. E ec s o ligh on seag ass
pho osyn hesis, g ow h and dep h dis ibu ion.
Aqua ic Bo any 27, 15-26.
h ps://doi.o g/10.1016/0304-3770(87)90083-0
Dewi CSU, Sukanda . 2017. Impo an alue index
and biomass (es ima ion) o seag ass on Talango
Island, Sumenep, Madu a. AIP Con e ence
P oceedings 1908, 030005.
h ps://doi.o g/10.1063/1.5012705
Do y MS. 1971 Measu emen o wa e mo emen in
e e ence o ben hic ma ine algal g ow h. Bo anica
Ma ina 14, 32–35.
h ps://doi.o g/10.1515/bo m.1971.14.1.32
Dua e CM, Chiscano CL. 1999. Seag ass biomass
and p oduc ion: a eassessmen . Aqua ic Bo any 65,
159-174.
h ps://doi.o g/10.1016/s0304-3770(99)00038-8
Dua e CM, Te ados J, Agawin NSR, Fo es
MD, Bach S, Kenwo hy WJ. 1997. Response o a
mixed Philippine seag ass meadow o expe imen al
bu ial. Ma ine Ecology P og ess Se ies 147, 285-294.
h ps://doi.o g/10.3354/meps147285
Dua e CM, Middlebu g J, Ca aco N. 2005.
Majo ole o ma ine ege a ion on he oceanic ca bon
cycle. Biogeosciences 2, 1-8.
h ps://doi.o g/10.5194/bg-2-1-2005
Dua e CM. 1991. Allome ic scaling o seag ass
o m and p oduc i i y. Ma ine Ecology P og ess
Se ies 77, 289-300.
h ps://doi.o g/10.3354/meps077289
Dua e CM. 1995. Subme ged aqua ic ege a ion in
ela ion o di e en nu ien egimes. Ophelia 41,
87–112.
h ps://doi.o g/10.1080/00785236.1995.10422039
Dua e CM, Te ados J, Agawin NSR, Fo es
MD. 2000. An expe imen al es o he occu ence o
compe i i e in e ac ions among SE Asian seag asses.
Ma ine Ecology P og ess Se ies 197, 231–240.
h ps://doi.o g/10.3354/meps197231
Du y JE. 2006. Biodi e si y and he unc ioning o
seag ass ecosys ems. Ma ine Ecology P og ess Se ies
311, 233-250.
h ps://doi.o g/10.3354/meps311233
E emeije PLA, He man PMJ. 1994. Seasonal
changes in en i onmen al a iables, biomass,
p oduc ion and nu ien con en s in wo con as ing
opical in e idal seag ass beds in Sou h Sulawesi,
87
Hamisain e al.
In . J. Biosci.
2020
Indonesia. Oecologia 99, 45-49.
h ps://doi.o g/10.1007/b 00317082
Fe ei a C, Simioni C, Schmid EC, Ramlo F,
Ma aschin M, Bouzon ZL. 2017. The in luence o
salini y on g ow h, mo phology, lea ul as uc u e,
and cell iabili y o he seag ass Halodule w igh ii
Asche son. P o oplasma 254, 1529–1537.
h ps://doi.o g/10.1007/s00709-016-1041-4
Fo es, MD. 1995. Seag asses o Eas Asia:
En i onmen al and managemen pe spec i es.
RCU/EAS Technical Repo Se ies No. 6. Uni ed
Na ions En i onmen P og amme, Bangkok, 75 pp.
G assho K, K emling K, Eh ha d M. 1983.
Me hods o seawa e analysis. Ve l. Chemie,
Weinheim, 419 p.
G een EP, Sho FT. 2003. Wo ld A las o
Seag asses. Uni e si y o Cali o nia P ess, Be keley,
p. 298.
G e e T, Binze T. 2004. Which ac o s egula e
seag ass g ow h and dis ibu ion? In: Bo um J,
Dua e CM, K ause-Jensen D, G e e TM, edi o s.
Eu opean seag asses: an in oduc ion o moni o ing
and managemen . The Moni o ing and Managemen
o Eu opean Beds P ojec . 2004. p. 19-23.
Gulls öm M, de la To e C, Bandei a SO,
Bjö k M, Dahlbe g M, Kau sky N, Rönnback P,
Őhman MC. 2002. Seag ass ecosys ems in he
Wes e n Indian Ocean. AMBIO A Jou nal o he
Human En i onmen 31(7-8), 588-596.
h ps://doi.o g/10.1579/0044-7447-31.7.588
Ha lin MM, Tho ne-Mille B. 1981. Nu ien
en ichmen o seag ass beds in a Rhode Island coas al
lagoon. Ma ine Biology 65, 221-229.
h ps://doi.o g/10.1007/b 00397115
Hillman K, Walke DI, La kum AWD,
McComb AJ. 1989. P oduc i i y and nu ien
limi a ion. In: La kum AWD, McComb AJ, Shephe d
SA (Eds.). Biology o Seag asses: A T ea ise on he
Biology o Seag asses wi h Special Re e ence o he
Aus alian Region. Else ie , Ams e dam. pp. 635-685.
Iizumi H, Ha o i A, McRoy CP. 1982.
Ammonium egene a ion and assimila ion in eelg ass
(Zos e a ma ina) beds. Ma ine Biology 66, 59-65.
h ps://doi.o g/10.1007/b 00397255
Kuo J, den Ha og C. 2001. Seag ass axonomy
and iden i ica ion key. In: Sho FT, Coles RG (Eds.).
Else ie , Ams e dam. pp. 31-58.
Kuo J, den Ha og C. 2006. Seag ass mo phology,
ana omy, and ul as uc u e. In: La kum AWD, O h
RJ, Dua e CM (Eds.). Seag asses: Biology, Ecology
and Conse a ion. Sp inge . pp. 51-87.
Lee K-S, Dun on KH. 1996. P oduc ion and ca bon
ese e dynamics o he seag ass Thalassia
es udinum in Co pus Ch is i Bay, Texas, USA.
Ma ine Ecology P og ess Se ies 143, 201-201.
h ps://doi.o g/10.3354/meps143201
Lee K-S, Dun on KH. 2000. E ec s o ni ogen
en ichmen on biomass alloca ion, g ow h, and lea
mo phology o he seag ass Thalassia es udinum.
Ma ine Ecology P og ess Se ies 196, 39-48.
h ps://doi.o g/10.3354/meps196039
Lee K-S, Pa k SR, Kim JB. 2005. P oduc ion
dynamics o he eelg ass, Zos e a ma ina in wo bay
sys ems on he sou h coas o he Ko ean peninsula.
Ma ine Biology 147, 1091-1108.
h ps://doi.o g/10.1007/s00227-005-0011-8
Lin HJ, Shao KT. 1998. Tempo al changes in he
abundance and g ow h o in e idal Thalassia
hemp ichii seag ass beds in sou he n
Taiwan. Bo anical Bulle in o Academia Sinica 39,
191-198.
Lin HJ, Hsieh LY, Liu PJ. 2005. Seag asses o
Tongsha Island, wi h desc ip ions o ou new eco ds
o Taiwan. Bo anical Bulle in o Academia Sinica 46,
88
Hamisain e al.
In . J. Biosci.
2020
163-168.
Ma co-Méndez C, Fe e o-Vicen e LM. P ado
P, Heck KLJ, Ceb ián J, Sánchez-Lizaso JL.
2015. Epiphy e p esence and seag ass species iden i y
in luence a es o he bi o y in Medi e anean
seag ass meadows. Es ua ine Coas al Shel Science
154, 94-101.
h ps://doi.o g/10.1016/j.ecss.2014.12.043
McRoy CP, McMillan C. 1997. P oduc ion ecology
and physiology o seag ass. In: McRoy CP, Hel e ich
C (Eds.). Seag ass Ecosys ems: a Scien i ic
Pe spec i e. Dekke , New Yo k, p 53-81.
Meñez E, Phillips R, Calumpong H. 1983.
Seag asses om he Philippines. Washing on:
Smi hsonian Ins i u ion P ess.
h ps://doi.o g/10.5479/si.01960768.21
Mu ay L, Dennison WC, Kemp WM. 1992.
Ni ogen e sus phospho us limi a ion o g ow h o
an es ua ine popula ion o eelg ass (Zos e a ma ina
L.). Aqua ic Bo any 44, 83-100.
h ps://doi.o g/10.1016/0304-3770(92)90083-u
O h RJ, Ca u he s TJB, Dennison WC,
Dua e CM, Fou qu ean JW, Heck KLJ,
Hughes AR, Kend ick GA, Kenwo hy WJ,
Olya nik S, Sho FT, Wayco M, Williams SL.
2006. A global c isis o seag ass ecosys ems.
Bioscience 56, 987-996.
h ps://doi.o g/10.1641/0006-
3568(2006)56[987:agc se]2.0.co;2
O h RJ. 1977. The impo ance o sedimen s abili y
in seag ass communi ies. In: Coull BC (Ed.). Ecology
o Ma ine Ben hos. Uni e si y o Sou h Ca olina
P ess, Columbia. P 281-300.
Pe ez M, Rome o J, Dua e CM, Sand-Jensen
K. 1991. Phospho us limi a ion o Cymodocea nodosa
g ow h. Ma ine Biology 109, 129-133.
h ps://doi.o g/10.1007/b 01320239
Phillips RC, Meñez EG. 1988. Seag asses.
Washing on DC: Smi hsonian Con ibu ions o he
Ma ine Sciences.
h ps://doi.o g/10.5479/si.01960768.34
Phillips RC, San elices B, B a o R, McRoy CP.
1983. He e ozos e a asmanica (Ma ens ex Asche s)
den Ha og in Chile. Aqua ic Bo any 15, 195-200.
h ps://doi.o g/10.1016/0304-3770(83)90029-3
Powell GVN, Kenwo hy WJ, Fou qu ean JW.
1989. Expe imen al e idence o nu ien limi a ion
o seag ass g ow h in a opical es ua y wi h es ic ed
ci cula ion. Bulle in Ma ine Science 44, 324-340.
P a hep A. 2003. Spa ial and empo al a ia ions in
pe cen age co e o wo common seag asses a
Si ina Na ional Pa k, Phuke ; and a i s s ep o
ma ine base. Songklanaka in Jou nal o Science and
Technology 25 (5), 651-658.
Ranahewa TH, Gunaseka a AJM,
P ema a hna AD, Ka una a hna SC,
Jayamanne SC. 2018. A compa a i e s udy on he
di e si y o seag ass species in selec ed a eas o
Pu alam lagoon in S i Lanka. Jou nal o
Oceanog aphy and Ma ine Resea ch 6(3), 1-6.
h ps://doi.o g/10.4172/2572-3103.1000185
Sama akoon JI, Van Zon H. 1991. En i onmen al
p o ile o Mu hu ajawela and Negombo lagoon. The
Ne he lands: Eu oconsul and Colombo: G ea e
Colombo Economic Commission. 173 p.
Sho FT, Coles RG. 2001. Global Seag ass
Resea ch Me hods. Else ie , Ams e dam. 482 p.
Sho FT, Dennison WC, Capone DG. 1990.
Phospho us-limi ed g ow h o he opical seag ass
Sy ingodium ili o me in ca bona e sedimen s.
Ma ine Ecology P og ess Se ies 62, 169-174.
h ps://doi.o g/10.3354/meps062169
Sho FT, Ca u he s TJB, Dennison WC,
Wayco M. 2007. Global seag ass dis ibu ion and