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ISSN: 2320-7078
Volume 1 Issue 3
Online Available at www.entomoljournal.com
Journal of Entomology and Zoology Studies
Vol. 1 No. 3 2013 www.entomoljournal.com Page | 47
Marine Meiofauna in Songculan Lagoon, Songculan, Dauis,
Bohol Philippines
Hongayo, Menelo C 1*
, Abad, Lawrence Alvir A1
., Acuesta, Tara R1
., Ayeng, Ted Mikko A1
., Cano, Vincent Nino
V1
., Guioguio Enrique A1
., Lingas Jarryn M1
., Vito Margie P 1
1. Field biology (Bio 10) 2012, Mathematics and Natural Sciences Department, College of Arts and Sciences,
Holy Name University, Tagbilaran City Bohol, Philippines.
[E-mail: menelo20022003@yahoo.com; Tel: 639177321085 ]
Meiofaunal organisms are small animals found living in the benthic zones of both freshwater and marine habitats
and are considered numerically dominant metazoans. Their presence in the benthic zone is important since they
serve as links to higher trophic levels in the ecosystems. This study aimed to identify meiofaunal organisms found in
Songculan Lagoon, Songculan Dauis, Bohol, Philippines; determine the physico – chemical properties of water and
sediments in Songculan Lagoon; and compute and compare for relative abundance of the meiofaunal taxa. This
study was limited to meiofaunal taxa identification up to class level. Sampling involves coring method [2, 9]
. The
results identified eleven (11) meiofaunal taxa namely; Nematoda, Copepod, Ostracod, Turbellaria, Gastropod,
Flatworms, Gastrotricha, Polychaeta, Oligochaeta, Rotifera and Tardigrada.
Keyword: Meiofaunal organisms, Marine habitats, Metazoans
1. Introduction
Meiofaunal organisms are small animals (pass
through a .500 mm sieve and are retained on a
0.063 or 0.045 mm sieve) [1]
, found living in the
benthic zones of both freshwater and marine
habitats and are considered numerically dominant
metazoans. They occur from the splash zone on
the beach to the deepest sediments in the sea, and
found on all types of sediments. Their sizes are
intermediate with that of the macrofauna and
microfauna [2, 3, 4]
. Due to their taxonomic
diversity and species richness, meiofauna
represent an important but often neglected
component of marine biodiversity.
About twenty – three higher taxa of the thirty –
three metazoan phyla have some meiobenthic
representatives. Some of these taxa are
exclusively meiobenthic, like Gastrotricha,
Kinorhyncha, Loricifera, Nematode, Turbellaria,
Oligochaeta, Polychaeta, Copepoda, Ostracoda,
Mystacocarida, Halacuroidea, Hydrozoa,
Nemertina, Entoprocta, Gastropoda,
Aplacophora, Brachiopoda, Holothuroidea,
Tunicata, Priapulida, Sipunculida wherein other
taxa are meiobenthic in certain point in their life
history [2]
. To date, 390 of the approximate 700
described are exclusively marine species, with the
remainder known from various freshwater
habitats [5]
. Despite its taxonomic heterogeneity,
meiofauna are believed to belong to a separate
functional group of marine benthos [4]
.
With these, their presence of these interstitial
organisms in the benthic zone is important since
they serve as links to higher trophic levels in the
marine ecosystems. They play an important role
in bioturbation and stimulation of bacterial
metabolism in marine sediments [2]
. They also
participate in the biomineralization of organic
matter particularly the sediments and act as a link
between detritus and higher trophic levels in
Journal of Entomology and Zoology Studies
Vol. 1 No. 3 2013 www.entomoljournal.com Page | 48
tropical habitats. This also exhibit high sensitivity
to anthropogenic inputs, making them excellent
sentinels of pollution [6]
. Futhermore, the
importance of meiofauna on ecosystem dynamics
and the lack of background information on them
suggest the creation of baseline research [7]
and
will provide the first steps for a comprehensive
understanding of the effect of habitat loss and
fragmentation, since the state and composition of
meiofauna assemblages may reflect the general
health of the marine benthos [8]
.
2. Objectives of the Study
This study aimed to identify possible meiofaunal
organisms found in Songculan Lagoon,
Songculan Dauis, Bohol, Philippines; determine
the physico – chemical properties of water and
sediments in Songculan Lagoon; and compute for
relative abundance of the meiofaunal taxa.
3. Significance of the Study
The main importance of this study is to identify
the meiofaunal taxa in Songculan Lagoon. The
results of this study serve as baseline information
of the meiofaunal taxa and their abundance. This
raised awareness of the importance of these
interstitial organisms in Songculan Lagoon so
that activities that directly or indirectly cause
disturbance will be taken into consideration. The
importance of meiofauna on ecosystem dynamics
and the lack of background information on them
suggest the creation of baseline research, which
`provide the first steps for a comprehensive
understanding of the effect of habitat loss, and
fragmentation, since the state and composition of
meiofauna assemblages may reflect the general
health of the marine benthos [7]
.
4. Scope and Limitations of the Study
This study was limited to meiofauna taxa
identification up to class level in Songculan
Lagoon. The sampling was conducted last July
25, 2012. Sampling involved coring method[2]
.
Salinity and temperature were the only physical
parameters taken. The variables measured for
water analysis included density, temperature,
turbidity, salinity, suspended solids, color and
pH.
5. Materials and Methods
5.1 Sampling site
Three stations were selected, station 1- one near
the mouth (9° 38'9'' N, 123°50'18'' E), station 2-
in the middle (9°38'8" N, 123°50'13'' E) and
station 3-the other one in the end (9°38'5'' N,
123°50'7'' E) of Songculan Lagoon in Songculan,
Dauis, Bohol Philippines with dense mangrove
populations on the edges.
Fig 1: Songculan Lagoon
5.2 Sample collection, fixation, extraction and
identification
Sediment samples were collected during low tide
in the intertidal zone through coring method [2,9]
and fixed in 5% buffered formalin stained with
congo red. Extraction was conducted through
decantation [2]
. The collected meiofaunal
organisms were examined and identified under
the use of stereoscope using pictorial key
identification.
5.3 Sediment Analysis
The samples were dried at 60º C, weighed and
then sieved (sieves 75 µm and 150 µm). The
sediments that were able to pass through each
sieve were weighed and computed for % sand, %
silt, % clay [8]
.
5.4 Data Analysis
In this particular study, in determining the
abundance, the formula of Smith and Smith [10]
,
was used
=
Journal of Entomology and Zoology Studies
Vol. 1 No. 3 2013 www.entomoljournal.comPage | 49
and to compare the abundance was analyzed with
Kolmogorov-Smirnov Two Sample Test for the
comparison among taxa. The significance level
was set at P<0.05.
6. Results and Discussion
Table 1: Relative abundance of meiofaunal taxa in Songculan Lagoon
Meiofauna
Station 1 Station 2 Station 3
R1 R2 R3
Abundance
Relative
Abundance
(%)
R1 R2 R3
Abundance
Relative
Abundance
(%)
R1 R2 R3
Abundance
Relaive
Abundance
(%)
Abundance
Relative
Abundance
(%)
Tardigrada 1 0 0 1 0% 7 0 0 7 1% 0 0 0 0 0% 8 0%
Rotifera 0 0 0 0 0% 0 0 0 0 0% 9 2 2 13 3% 13 1%
Oligochaeta 0 0 0 0 0% 11 0 8 19 3% 0 0 0 0 0% 19 1%
Polychaeta 4 1 0 5 1% 0 0 0 0 0% 0 10 6 16 4% 21 1%
Gastroticha 0 0 0 0 0% 0 0 0 0 0% 0 12 10 22 5% 22 1%
Flatworms 0 0 0 0 0% 24 8 8 40 7% 0 0 0 0 0% 40 2%
Gastropod 2 0 1 3 0% 15 2 9 26 5% 47 56 50 153 38% 182 11%
Turbellaria
84 87 70 241
36
%
0 0 0 0 0% 0 0 0 0 0% 241 15%
Ostracod
79 72 20 171
26
%
30 8 49 87 15% 0 0 0 0 0% 258 16%
Copepod 0 0 0 0 0% 62 101 111 274 48% 1 5 2 8 2% 282 17%
Nematodes
92 76 74 242
37
%
40 42 34 116 20% 43 75 76 194 48% 552 34%
663 569 406 1638
Table 2: Kolmogorov-Smirnov Two Sample Test of Meiofaunal taxa in Songculan Lagoon
Meiofauna
Nematodes
Oligochaet
a
Tardigrad
a
Copepod
Ostracod
Gastropod
Polychaeta
Rotifera
Gastrotich
a
Turbellari
a
Flatworms
Nematodes 1
Oligochaeta 0 1
Tardigrada 0 0.966 1
Copepod 0.028 0.307 0.307 1
Ostracod 0.028 0.111 0.028 0.662 1
Gastropod 0.028 0.028 0.028 0.662 0.966 1
Polychaeta 0 0.966 0.966 0.662 0.111 0.307 1
Rotifera 0 1 0.966 0.662 0.111 0.111 0.966 1
Gastroticha 0 1 0.966 0.307 0.111 0.028 0.966 0.966 1
Turbellaria 0.028 0.662 0.662 0.662 0.662 0.111 0.662 0.662 0.662 1
Flatworms 0 1 0.662 0.662 0.307 0.111 0.966 0.966 1 0.662 1
Fig 2: Relative abundance of meiofaunal taxa in Songculan Lagoon Songculan Dauis Bohol Philippines.
0% 10% 20% 30% 40%
Tardigrada
Oligochaeta
Gastroticha
Gastropod
Ostracod
Nematodes
Relative Abundance
Relative Abundance
Journal of Entomology and Zoology Studies
Vol. 1 No. 3 2013 www.entomoljournal.com Page | 50
Fig 2: Meiofaunal Organisms in Songculan Lagoon, Songculan Dauis Bohol Philippines.
Table 3: Physico-chemical properties of seawater in Songculan Lagoon, Songculan Dauis Bohol Philippines.
Properties
Temperature Salinity pH Turbidity Density Color Suspended solids(100ml)
30°C 31.5ppt 8 (Basic) 30cm+++ 100.415g/ml Clear 8.75
Table 4: Sediment analysis in Songculan Lagoon, Songculan Dauis Bohol Philippines.
Wet Wt.
Dry Wt. 184.3 g
Sand Silt Clay
195.4 g 149.5g (81%) 28.9 g (16%) 5.9 g (3%)
Eleven (11) meiofaunal taxa were identified in
Songculan Lagoon namely; Netamoda, Copepod,
Ostracod, Turbellaria, Gastropod, Flatworms,
Gastroticha, Polychaeta, Oligochaeta, Rotifera
and Tardigrada. In station 1, six (6) meiofanual
taxa determined which included the Tardigrada,
Polychaeta, Gastropod, Turbellaria, Ostracod, and
Nematodes. For station 2, seven (7) taxa were
determined having the highest number taxa in
Songculan Lagoon namely Tardigrada,
Oligochaeta, Flatworms, Gastropod, Ostracod,
Copepod and Nematodes. In station 3 with six (6)
taxa which included the Rotifera, Polychaeta,
Gastroticha, Gastropod, Copepod and
Nematodes. Nematodes and Garstropods were
the taxa occurring in all stations.
The most dominant at the entire sampling site
were the Nematodes as shown in Table 1 and
Figure 2. Table 1 showed the relative abundance
or dominant of meiofaunal taxa found among
sediments in Songculan Lagoon namely;
Netamoda (34%-552 individuals), Copepod
(17%-282 individuals), Ostracod (16%-258
individuals), Turbellaria (15%-241 individuals),
Gastropod (11%-182 individuals), Flatworms
(2%-40 individuals), Gastroticha (1%-22
individuals), Polychaeta (1%-21 individuals),
Oligochaeta (1-%19 individuals), Rotifera (1%-
13 individuals) and Tardigrada (0%-8
individuals).
In the Kolmogorov-Smirnov Two Sample Test as
shown in Table 2 for the comparison of the
abundance of meiofauna taxa, for Nematoda that
there was a significant difference compared
among meiofauna taxa identified in this study.
For Oligochaeta, there was a significant
difference compared to Nematoda (P>0.05) and
Gastropoda (P>0.028). For Tardigrada, there was
Journal of Entomology and Zoology Studies
Vol. 1 No. 3 2013 www.entomoljournal.comPage | 51
a significant difference compared to Ostracod
(P>0.028) and Nematoda (P>0.05). For
Ostracoda, there was a significant difference
compared to Nematoda (P>0.05) and Tardigrada
(P>0.028). For Gastropod, there was a significant
difference compared to Nematoda (P>0.05),
Oligochaeta (P>0.028) and Gastroticha
(P>0.028). For Gastroticha, there was a
significant difference compared to Nematoda
(P>0.05) and Gastropod (P>0.028). For Copepod,
Flatworms, Polychaeta, Rotifera and Turbellaria,
there was no significant difference among
meiofauna taxa except for Nematoda (P>0.05).
The abundance of the interstitial organisms in
Songculan Lagoon could be associated to the
following environmental factors: grain size,
circulation of water, temperature, salinity and
wave action.
In this study sediment analysis was conducted, it
was found out that the sediments were composed
of 81% sand, 16% silt and 3 % clay. Having this
type this would unable to hold-in water when
tides ebbs leaving. This could explain the
abundance of nematodes identified with 34% of
relative abundance (552 individuals) like in the
study of Gheskiere [8]
, that these are slender and
adapted to live in small water-filled interstitial
spaces like the fine grain sized sandy beaches are
suitable environments. In addition, according the
Nybakken [11]
, nematodes are most abundant and
diversed interstitial organism. This could be
explain to the abundance of the crustacean
representative the Copepod and Ostracod,
Turbellaria, Gastropod, Flatworms, Gastroticha,
Polychaeta, Oligochaeta, Rotifera and Tardigrada
in relation to their sediment type preference.
Circulation of water through pore spaces in
sediments is an important factor because this is
responsible for water movement in renewing the
oxygen supply [11]
. This circulation is ideal to
coarse type of sediment like documented in this
study as shown in Table 4.
Furthermore, with some limitations of the
procedure and equipments used in this study
eleven 11 taxa of interstitial organisms from the
three (3) sample stations were identified. For
future studies more sampling stations should be
selected inorder to show the clearer picture of
how diverse the meiofaunal organisms that are
found in Songculan Lagoon, Songculan, Dauis,
Bohol, Philippines.
7. Acknowledgement
Mathematics and Natural Sciences Department,
College of Arts and Sciences, Holy Name
University, Tagbilaran City Bohol, Philippines
LGU, Songculan, Dauis Bohol, Philippines
MCH CO.
8. References
1. Meiofauna.org. What is meiobenthology?,
http://www.meiofauna.org/index.html. 6
September, 2012.
2. Vincx M. Meiofauna in marine and freshwater
sediments. Cab International, Belgium, 1996, 187-
195.
3. Funch P, Neilsen NEN, Graf S, Buttler F. Marine
Meiofauna. Feltkursus i videregående zoologi på
molslaboratoriet. Denmark 2002.
4. Kotwicki L, Szymelfenig M, De Troch M, Urban-
Malinga B, Weslawski JM. Latitudinal biodiversity
patterns of meiofauna from sandy littoral beaches.
Biodiversity and Conservation 2008; 14: 461–474.
5. Hochberg R. Gastroticha of Bocas del Toro Panama:
A preliminary report. Mei mar Germany, 2008, 16:
101-107.
6. Kotwicki L, Meiofauna of Sandy Beaches,.
http://www.marbef.org/wiki/Meiofauna_of_Sandy_
Beaches. 2009
7. Armenteros M, Creaghand B, González Sansón G.
Distribution patterns of the meiofauna in coral reefs
from the NW shelf of Cuba. Rev Invest 2009; 30(1):
37-38.
8. Gheskiere T, Hoste E, Kotwicki L, Degraer S,
Verbeke JV, Vincx M. The sandy beach meiofauna
and free-living nematodes from De Panne
(Belgium). Biologie 2002; 72-Supp:43-49.
9. Chindah A, Braide S. Meiofauna occurrence and
distribution in different substrate types of bonny
brackish wetland of the Niger Delta. JASEM 2001; 5
(1):33-41.
10. Smith R, Smith T. Elements of Ecology. Ed 4,
Addison Wesley Longman Inc., USA, 2000, 450.
11. Nybakken J. Marine Biology an Ecological approach.
Ed 4, Addison-Wesley Educational Publishers Inc,
1997, 989.

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  • 1. ISSN: 2320-7078 Volume 1 Issue 3 Online Available at www.entomoljournal.com Journal of Entomology and Zoology Studies Vol. 1 No. 3 2013 www.entomoljournal.com Page | 47 Marine Meiofauna in Songculan Lagoon, Songculan, Dauis, Bohol Philippines Hongayo, Menelo C 1* , Abad, Lawrence Alvir A1 ., Acuesta, Tara R1 ., Ayeng, Ted Mikko A1 ., Cano, Vincent Nino V1 ., Guioguio Enrique A1 ., Lingas Jarryn M1 ., Vito Margie P 1 1. Field biology (Bio 10) 2012, Mathematics and Natural Sciences Department, College of Arts and Sciences, Holy Name University, Tagbilaran City Bohol, Philippines. [E-mail: menelo20022003@yahoo.com; Tel: 639177321085 ] Meiofaunal organisms are small animals found living in the benthic zones of both freshwater and marine habitats and are considered numerically dominant metazoans. Their presence in the benthic zone is important since they serve as links to higher trophic levels in the ecosystems. This study aimed to identify meiofaunal organisms found in Songculan Lagoon, Songculan Dauis, Bohol, Philippines; determine the physico – chemical properties of water and sediments in Songculan Lagoon; and compute and compare for relative abundance of the meiofaunal taxa. This study was limited to meiofaunal taxa identification up to class level. Sampling involves coring method [2, 9] . The results identified eleven (11) meiofaunal taxa namely; Nematoda, Copepod, Ostracod, Turbellaria, Gastropod, Flatworms, Gastrotricha, Polychaeta, Oligochaeta, Rotifera and Tardigrada. Keyword: Meiofaunal organisms, Marine habitats, Metazoans 1. Introduction Meiofaunal organisms are small animals (pass through a .500 mm sieve and are retained on a 0.063 or 0.045 mm sieve) [1] , found living in the benthic zones of both freshwater and marine habitats and are considered numerically dominant metazoans. They occur from the splash zone on the beach to the deepest sediments in the sea, and found on all types of sediments. Their sizes are intermediate with that of the macrofauna and microfauna [2, 3, 4] . Due to their taxonomic diversity and species richness, meiofauna represent an important but often neglected component of marine biodiversity. About twenty – three higher taxa of the thirty – three metazoan phyla have some meiobenthic representatives. Some of these taxa are exclusively meiobenthic, like Gastrotricha, Kinorhyncha, Loricifera, Nematode, Turbellaria, Oligochaeta, Polychaeta, Copepoda, Ostracoda, Mystacocarida, Halacuroidea, Hydrozoa, Nemertina, Entoprocta, Gastropoda, Aplacophora, Brachiopoda, Holothuroidea, Tunicata, Priapulida, Sipunculida wherein other taxa are meiobenthic in certain point in their life history [2] . To date, 390 of the approximate 700 described are exclusively marine species, with the remainder known from various freshwater habitats [5] . Despite its taxonomic heterogeneity, meiofauna are believed to belong to a separate functional group of marine benthos [4] . With these, their presence of these interstitial organisms in the benthic zone is important since they serve as links to higher trophic levels in the marine ecosystems. They play an important role in bioturbation and stimulation of bacterial metabolism in marine sediments [2] . They also participate in the biomineralization of organic matter particularly the sediments and act as a link between detritus and higher trophic levels in
  • 2. Journal of Entomology and Zoology Studies Vol. 1 No. 3 2013 www.entomoljournal.com Page | 48 tropical habitats. This also exhibit high sensitivity to anthropogenic inputs, making them excellent sentinels of pollution [6] . Futhermore, the importance of meiofauna on ecosystem dynamics and the lack of background information on them suggest the creation of baseline research [7] and will provide the first steps for a comprehensive understanding of the effect of habitat loss and fragmentation, since the state and composition of meiofauna assemblages may reflect the general health of the marine benthos [8] . 2. Objectives of the Study This study aimed to identify possible meiofaunal organisms found in Songculan Lagoon, Songculan Dauis, Bohol, Philippines; determine the physico – chemical properties of water and sediments in Songculan Lagoon; and compute for relative abundance of the meiofaunal taxa. 3. Significance of the Study The main importance of this study is to identify the meiofaunal taxa in Songculan Lagoon. The results of this study serve as baseline information of the meiofaunal taxa and their abundance. This raised awareness of the importance of these interstitial organisms in Songculan Lagoon so that activities that directly or indirectly cause disturbance will be taken into consideration. The importance of meiofauna on ecosystem dynamics and the lack of background information on them suggest the creation of baseline research, which `provide the first steps for a comprehensive understanding of the effect of habitat loss, and fragmentation, since the state and composition of meiofauna assemblages may reflect the general health of the marine benthos [7] . 4. Scope and Limitations of the Study This study was limited to meiofauna taxa identification up to class level in Songculan Lagoon. The sampling was conducted last July 25, 2012. Sampling involved coring method[2] . Salinity and temperature were the only physical parameters taken. The variables measured for water analysis included density, temperature, turbidity, salinity, suspended solids, color and pH. 5. Materials and Methods 5.1 Sampling site Three stations were selected, station 1- one near the mouth (9° 38'9'' N, 123°50'18'' E), station 2- in the middle (9°38'8" N, 123°50'13'' E) and station 3-the other one in the end (9°38'5'' N, 123°50'7'' E) of Songculan Lagoon in Songculan, Dauis, Bohol Philippines with dense mangrove populations on the edges. Fig 1: Songculan Lagoon 5.2 Sample collection, fixation, extraction and identification Sediment samples were collected during low tide in the intertidal zone through coring method [2,9] and fixed in 5% buffered formalin stained with congo red. Extraction was conducted through decantation [2] . The collected meiofaunal organisms were examined and identified under the use of stereoscope using pictorial key identification. 5.3 Sediment Analysis The samples were dried at 60º C, weighed and then sieved (sieves 75 µm and 150 µm). The sediments that were able to pass through each sieve were weighed and computed for % sand, % silt, % clay [8] . 5.4 Data Analysis In this particular study, in determining the abundance, the formula of Smith and Smith [10] , was used =
  • 3. Journal of Entomology and Zoology Studies Vol. 1 No. 3 2013 www.entomoljournal.comPage | 49 and to compare the abundance was analyzed with Kolmogorov-Smirnov Two Sample Test for the comparison among taxa. The significance level was set at P<0.05. 6. Results and Discussion Table 1: Relative abundance of meiofaunal taxa in Songculan Lagoon Meiofauna Station 1 Station 2 Station 3 R1 R2 R3 Abundance Relative Abundance (%) R1 R2 R3 Abundance Relative Abundance (%) R1 R2 R3 Abundance Relaive Abundance (%) Abundance Relative Abundance (%) Tardigrada 1 0 0 1 0% 7 0 0 7 1% 0 0 0 0 0% 8 0% Rotifera 0 0 0 0 0% 0 0 0 0 0% 9 2 2 13 3% 13 1% Oligochaeta 0 0 0 0 0% 11 0 8 19 3% 0 0 0 0 0% 19 1% Polychaeta 4 1 0 5 1% 0 0 0 0 0% 0 10 6 16 4% 21 1% Gastroticha 0 0 0 0 0% 0 0 0 0 0% 0 12 10 22 5% 22 1% Flatworms 0 0 0 0 0% 24 8 8 40 7% 0 0 0 0 0% 40 2% Gastropod 2 0 1 3 0% 15 2 9 26 5% 47 56 50 153 38% 182 11% Turbellaria 84 87 70 241 36 % 0 0 0 0 0% 0 0 0 0 0% 241 15% Ostracod 79 72 20 171 26 % 30 8 49 87 15% 0 0 0 0 0% 258 16% Copepod 0 0 0 0 0% 62 101 111 274 48% 1 5 2 8 2% 282 17% Nematodes 92 76 74 242 37 % 40 42 34 116 20% 43 75 76 194 48% 552 34% 663 569 406 1638 Table 2: Kolmogorov-Smirnov Two Sample Test of Meiofaunal taxa in Songculan Lagoon Meiofauna Nematodes Oligochaet a Tardigrad a Copepod Ostracod Gastropod Polychaeta Rotifera Gastrotich a Turbellari a Flatworms Nematodes 1 Oligochaeta 0 1 Tardigrada 0 0.966 1 Copepod 0.028 0.307 0.307 1 Ostracod 0.028 0.111 0.028 0.662 1 Gastropod 0.028 0.028 0.028 0.662 0.966 1 Polychaeta 0 0.966 0.966 0.662 0.111 0.307 1 Rotifera 0 1 0.966 0.662 0.111 0.111 0.966 1 Gastroticha 0 1 0.966 0.307 0.111 0.028 0.966 0.966 1 Turbellaria 0.028 0.662 0.662 0.662 0.662 0.111 0.662 0.662 0.662 1 Flatworms 0 1 0.662 0.662 0.307 0.111 0.966 0.966 1 0.662 1 Fig 2: Relative abundance of meiofaunal taxa in Songculan Lagoon Songculan Dauis Bohol Philippines. 0% 10% 20% 30% 40% Tardigrada Oligochaeta Gastroticha Gastropod Ostracod Nematodes Relative Abundance Relative Abundance
  • 4. Journal of Entomology and Zoology Studies Vol. 1 No. 3 2013 www.entomoljournal.com Page | 50 Fig 2: Meiofaunal Organisms in Songculan Lagoon, Songculan Dauis Bohol Philippines. Table 3: Physico-chemical properties of seawater in Songculan Lagoon, Songculan Dauis Bohol Philippines. Properties Temperature Salinity pH Turbidity Density Color Suspended solids(100ml) 30°C 31.5ppt 8 (Basic) 30cm+++ 100.415g/ml Clear 8.75 Table 4: Sediment analysis in Songculan Lagoon, Songculan Dauis Bohol Philippines. Wet Wt. Dry Wt. 184.3 g Sand Silt Clay 195.4 g 149.5g (81%) 28.9 g (16%) 5.9 g (3%) Eleven (11) meiofaunal taxa were identified in Songculan Lagoon namely; Netamoda, Copepod, Ostracod, Turbellaria, Gastropod, Flatworms, Gastroticha, Polychaeta, Oligochaeta, Rotifera and Tardigrada. In station 1, six (6) meiofanual taxa determined which included the Tardigrada, Polychaeta, Gastropod, Turbellaria, Ostracod, and Nematodes. For station 2, seven (7) taxa were determined having the highest number taxa in Songculan Lagoon namely Tardigrada, Oligochaeta, Flatworms, Gastropod, Ostracod, Copepod and Nematodes. In station 3 with six (6) taxa which included the Rotifera, Polychaeta, Gastroticha, Gastropod, Copepod and Nematodes. Nematodes and Garstropods were the taxa occurring in all stations. The most dominant at the entire sampling site were the Nematodes as shown in Table 1 and Figure 2. Table 1 showed the relative abundance or dominant of meiofaunal taxa found among sediments in Songculan Lagoon namely; Netamoda (34%-552 individuals), Copepod (17%-282 individuals), Ostracod (16%-258 individuals), Turbellaria (15%-241 individuals), Gastropod (11%-182 individuals), Flatworms (2%-40 individuals), Gastroticha (1%-22 individuals), Polychaeta (1%-21 individuals), Oligochaeta (1-%19 individuals), Rotifera (1%- 13 individuals) and Tardigrada (0%-8 individuals). In the Kolmogorov-Smirnov Two Sample Test as shown in Table 2 for the comparison of the abundance of meiofauna taxa, for Nematoda that there was a significant difference compared among meiofauna taxa identified in this study. For Oligochaeta, there was a significant difference compared to Nematoda (P>0.05) and Gastropoda (P>0.028). For Tardigrada, there was
  • 5. Journal of Entomology and Zoology Studies Vol. 1 No. 3 2013 www.entomoljournal.comPage | 51 a significant difference compared to Ostracod (P>0.028) and Nematoda (P>0.05). For Ostracoda, there was a significant difference compared to Nematoda (P>0.05) and Tardigrada (P>0.028). For Gastropod, there was a significant difference compared to Nematoda (P>0.05), Oligochaeta (P>0.028) and Gastroticha (P>0.028). For Gastroticha, there was a significant difference compared to Nematoda (P>0.05) and Gastropod (P>0.028). For Copepod, Flatworms, Polychaeta, Rotifera and Turbellaria, there was no significant difference among meiofauna taxa except for Nematoda (P>0.05). The abundance of the interstitial organisms in Songculan Lagoon could be associated to the following environmental factors: grain size, circulation of water, temperature, salinity and wave action. In this study sediment analysis was conducted, it was found out that the sediments were composed of 81% sand, 16% silt and 3 % clay. Having this type this would unable to hold-in water when tides ebbs leaving. This could explain the abundance of nematodes identified with 34% of relative abundance (552 individuals) like in the study of Gheskiere [8] , that these are slender and adapted to live in small water-filled interstitial spaces like the fine grain sized sandy beaches are suitable environments. In addition, according the Nybakken [11] , nematodes are most abundant and diversed interstitial organism. This could be explain to the abundance of the crustacean representative the Copepod and Ostracod, Turbellaria, Gastropod, Flatworms, Gastroticha, Polychaeta, Oligochaeta, Rotifera and Tardigrada in relation to their sediment type preference. Circulation of water through pore spaces in sediments is an important factor because this is responsible for water movement in renewing the oxygen supply [11] . This circulation is ideal to coarse type of sediment like documented in this study as shown in Table 4. Furthermore, with some limitations of the procedure and equipments used in this study eleven 11 taxa of interstitial organisms from the three (3) sample stations were identified. For future studies more sampling stations should be selected inorder to show the clearer picture of how diverse the meiofaunal organisms that are found in Songculan Lagoon, Songculan, Dauis, Bohol, Philippines. 7. Acknowledgement Mathematics and Natural Sciences Department, College of Arts and Sciences, Holy Name University, Tagbilaran City Bohol, Philippines LGU, Songculan, Dauis Bohol, Philippines MCH CO. 8. References 1. Meiofauna.org. What is meiobenthology?, http://www.meiofauna.org/index.html. 6 September, 2012. 2. Vincx M. Meiofauna in marine and freshwater sediments. Cab International, Belgium, 1996, 187- 195. 3. Funch P, Neilsen NEN, Graf S, Buttler F. Marine Meiofauna. Feltkursus i videregående zoologi på molslaboratoriet. Denmark 2002. 4. Kotwicki L, Szymelfenig M, De Troch M, Urban- Malinga B, Weslawski JM. Latitudinal biodiversity patterns of meiofauna from sandy littoral beaches. Biodiversity and Conservation 2008; 14: 461–474. 5. Hochberg R. Gastroticha of Bocas del Toro Panama: A preliminary report. Mei mar Germany, 2008, 16: 101-107. 6. Kotwicki L, Meiofauna of Sandy Beaches,. http://www.marbef.org/wiki/Meiofauna_of_Sandy_ Beaches. 2009 7. Armenteros M, Creaghand B, González Sansón G. Distribution patterns of the meiofauna in coral reefs from the NW shelf of Cuba. Rev Invest 2009; 30(1): 37-38. 8. Gheskiere T, Hoste E, Kotwicki L, Degraer S, Verbeke JV, Vincx M. The sandy beach meiofauna and free-living nematodes from De Panne (Belgium). Biologie 2002; 72-Supp:43-49. 9. Chindah A, Braide S. Meiofauna occurrence and distribution in different substrate types of bonny brackish wetland of the Niger Delta. JASEM 2001; 5 (1):33-41. 10. Smith R, Smith T. Elements of Ecology. Ed 4, Addison Wesley Longman Inc., USA, 2000, 450. 11. Nybakken J. Marine Biology an Ecological approach. Ed 4, Addison-Wesley Educational Publishers Inc, 1997, 989.