Journal of Environmental Treatment Techniques  
2020, Volume 3, Issue 3, Pages: 1176-1181  
J. Environ. Treat. Tech.  
ISSN: 2309-1185  
Journal web link: http://www.jett.dormaj.com  
Diversity of Gastropod and Bivalve Molluscs in  
Kaisu Mangrove Forest of Sarmi Regency, Papua  
Province, Indonesia  
*
Jacob Manusawai , Anton S. Sinery, Rina N. Jowey  
Department of Environmental Science, Universitas Papua, Indonesia  
Received: 13/05/2020  
Accepted: 22/07/2020  
Published: 20/09/2020  
Abstract  
Molluscs are an important part of the mangrove ecosystem. Scientific information related to gastropods and Bivalvia in Kaisu  
mangrove is not known. Thus, this study aims at identifying the diversity of molluscs (gastropod and Bivalvia) in Kaisu mangrove forest.  
This study has used descriptive method with observation techniques. The observation station was determined using purposive sampling  
considering the zonation of mangrove vegetation. The taken data were analyzed qualitatively and quantitatively based on each parameter.  
The results of the study show that, in Kaisu mangrove forest of Bongga District, Sarmi Regency, 10 species of molluscs were identified  
with 1804 individuals consisting of 8 species of gastropoda (Telescopium telescopium, Steno melani, Nerita articulate, Ellobiumaurisjudae,  
Cheritidea obtuse, Indothais gradate, Spherassimineamimata, Littorariamelanostoma) and 2 species of Bivalvia (Geloinaexpansa,  
Anumalocardisquamasa). The dominance index of the mollusca species of this mangrove forest was 0.74, indicating the dominance of  
Telescopium telescopium with species diversity index of 0.27 (low category) and a species evenness index of 0.32 (low category).  
Keywords: Molluscs; Bivalvia; Mangrove forest; Ecosystem  
Introduction1  
(
squid or chiton), Aplacophora and Monoplacopora. Bivalves  
1
play a vital role in the ecosystem of mangrove forest and in the  
lives of coastal humans (9). Bivalve molluscs are a valuable  
source of high-quality proteins, minerals and vitamins (10).  
Crustaceans and molluscs play important roles in the  
mangrove ecosystem, processing mangrove-derived and algal  
detritus through their feeding and bioturbation activities (11).  
According to Pramudji (12), Mollusca-inhabiting mangrove  
forests in Indonesia are generally dominated by gastropods,  
which are around 61 species. Gastropod in mangrove  
ecosystems has both ecological and economical significances.  
Gastropod (limpets, snails, whelks, slugs) is by far the most  
diverse group of molluscs with about 100,000 species (0.5 mm  
to 100 cm long) that inhabit all marine, freshwater and terrestrial  
habitats (13). From ecological perspective, gastropod is a type of  
fauna that have a role in a food chain. Gastropods are detritus-  
eaters that have function in tearing and minimizing newly fallen  
litter, and accelerating litter decompositions through  
microorganisms (12), (14). Gastropods have economic value as  
they are used by coastal community as food, for instance,  
The main text of the article should appear here. Headings  
and subheadings should be formatted using the relevant button  
from the “Apply Style” dialog box. Mangrove plays an  
important role in the lives of wildlife including birds, mammals,  
reptiles, fishes and other organisms such as mollusks (1). It is a  
biologically diverse ecosystem, rich in organic matter and  
nutrients, and supports a large biomass of flora and fauna (2). It  
is considered among the world’s most productive ecosystems  
(3). High rates of tree and plant growth, coupled with anaerobic,  
water-logged soils that slow decomposition, result in large long-  
term carbon © storage within the mangroves (4). From an  
economic point of view, mangroves have a very high economic  
and ecological value because of the wide range of ecosystem  
goods and services they offer (5).In addition, mangroves also  
perform, free-of-cost, many important functions that support the  
often-dense coastal populations (6). Molluscs are the second  
species-rich phylum in the world after arthropods (7). They are  
soft-bodied, unsegmented animals, with a body organized into a  
muscular foot, a head, a visceral mass containing most of the  
organ systems, and a fleshy mantle that secretes the calcareous  
shell(8). According to Brusca & Brusca (9), Mollusca consists of  
seven classes, namely Polyplacophora (chiton), Gastropod  
Terebraliapalustris,  
Telescopium  
telescopium,  
and  
Cerithideaobtusa (14). The total area of mangrove forests in  
Papua Island, including Papua and West Papua, is estimated to  
reach 1.3 million ha (1). The mangrove areas in Papua covers  
the North and South coasts of Papua Island, SaireriBay,  
Mamberamo River, HomblotBay, Wasoki Bay, Ansus, the  
Eastern part between Biak and Yapen Islands. In the Southern  
Part of West Papua, mangroves flourish along the Waigeo coast  
(snail), Bivalvia(clam), Scaphopoda (hornshell), Cephalopoda  
Corresponding author: Jacob Manusawai, Department of  
Environmental Science, Universitas Papua, Indonesia. E-mail:  
dr.jacob.manusawai@gmail.com  
1
176  
Journal of Environmental Treatment Techniques  
2020, Volume 3, Issue 3, Pages: 1176-1181  
and the northern part of Barai peninsula around Bintuni Bay;the  
mangroves in Bintuni are the most significant ecosystem in  
storing large amounts of carbon (15).  
2
where A is abundance (number of individual / 20m ); xi is  
number of individuals; and ni is number of squares. The  
concentration of individual species of Mollusca was determined  
using index of domination (C) as followed:  
Sarmi Regency has several locations of mangrove forests  
distribution, including along the East coast. The distribution of  
mangroves in the area is not only potentially related to  
ecological function but also related to the socio-economic  
conditions of the community. Ecologically, mangrove forest has  
an important role as a buffer zone which protects the coast from  
Pacific Ocean waves. Mangroves play an important role in  
buffering coastlines against storm surges and tsunamis through  
wave attenuation (16). For socio-economic matters, mangroves  
provide benefits for coastal communities’ livelihoods. The  
socio-economic value of the mangrove is likely to be more than  
double of the direct forest product value through the ecosystem  
linkage with the aquatic production and the effect on fishery  
2
ni   
C    
N   
where C is index of dominance; ni is number of individuals of a  
species; and n is number of individuals of all species.  
Domination is a community characteristic that shows the  
abundance of species in a region (22), (23), (24), (25). The  
criteria of domination index according to are as follows: 0 <C  
<0.5 = There are no dominant species; 0.5> C> 1 = There are  
dominant species. To determine the diversity of Mollusca as an  
indicator of habitat, species index diversity (H) according to  
Shanon and Wiener (1949) in Magurran (26) was used with the  
equation:  
(17). A number of potentials inhabiting fauna such as fish,  
shrimp, and crabs are an important part of the mangrove  
ecosystem. Similarly, Mollusca groups (gastropod and Bivalvia)  
also play an important role in mangrove ecosystem and people's  
lives. Yet, scientific information related to Mollusca groups in  
Kaisu mangrove is not known for certain. Therefore, the aim of  
the research is to examine the diversity of molluscs (gastropod  
and Bivalvia) in Kaisu mangrove forest.  
ni  
ni  
N
H    
ln  
N   
where H is diversity index (Shanon-weinner index); ni is number  
of individuals of a species, N is number of individuals of all  
species. The evenness of species of Mollusca at the study site  
was analyzed using the index of evenness (e), according to  
Pielou (27), Odum (23), and Bratawinata (28) as follows:  
2
Material and Methods  
The study was carried out in Kaisu mangrove (study area)  
forest in the District of Bonggo in Sarmi Regency, Papua  
Province of Indonesia in a span of two months. The equipment  
used to conduct the study were Global Positioning System,  
levers, plastics, collection bottles, tweezers, digital camera,  
Vernier caliper, surgical boards, gauges, raffia and stationery.  
This study used observation methods to conduct the  
research. Purposive sampling was used for observation station.  
The characteristics and species of Kaisu mangrove forest are  
relatively similar with a forest width of approximately 150-350  
H'  
H'  
e   
LogS Hmax  
Hmax  2 lns  
where e is species evenness index; H is species diversity index;  
S is number of species. Evenness index according to Krebs(29)  
in Sinery (30) ranged from 0-1, where: 0.6-1 = high species  
evenness; 0.4 <e <0.6 = moderate species evenness; 004 = low  
species evenness.  
m. Considering the condition,  
2 sampling stations were  
determined in one transect 320 m long with site I position (75 m  
from land-sea point) dominated by Rhizophorasp, Avicenniasp,  
Bruguera gymnorhiza), and site II (position 250 m from point 0  
or 175 m from site I which was presented by species like  
Rhizophorasp, Bruguera gymnorhiza and Sonneratiasp). Each  
site had one observation plot with size of 20 m × 20 m. To  
determine the species and number of individuals, variables such  
as morphological characters of molluscs (gastropod and  
Bivalvia) in the form of color and body size (length, width,  
diameter expressed in cm) were observed. General condition of  
the study site was documented.  
3
Results  
3
.1 Species Composition  
Based on identification of the morphological characteristics,  
0 species of Mollusca were identified in Kaisu mangrove area,  
1
i.e., 7 families and 8 species of gastropod, 2 families and 2  
species of bivalves (Table 1 and Table 2).  
3
.2 Domination, Diversity and Evenness Index of Mollusca  
This research used the dominance, diversity and evenness  
The samples of Mollusca (gastropod and Bivalvia) were  
collected at low tide and on sunny day. The collected samples  
were preserved using alcohol 70% and put into specimen box.  
The samples were identified using the journal (18), (19), (20),  
index to analyze the level of species domination, variation of  
species and evenness of species, as indicators of community  
stabilization in Kaisu mangrove forest. The dominance, diversity  
and evenness index of Mollusca species in Kaisu mangrove area  
are presented in the following Figure 1. The results of the study  
showed that Telescopium telescopium was the species with the  
highest number of individuals found at the study sites. In  
(21). The collected data were analyzed qualitatively and  
quantitatively based on each parameter and then presented in  
tables and figures (charts, graphs and photographs). To  
determine the abundance of species in the area, the equations  
was used as follows:  
comparison,  
the  
number  
of  
species  
such  
as Littorariamelanostoma and Anumalocardi,  
smaller in number.  
squamasa was  
xi  
A   
ni  
1
177  
Journal of Environmental Treatment Techniques  
2020, Volume 3, Issue 3, Pages: 1176-1181  
Table 1: Composition of Mollusca in Kaisu Mangrove Forest  
Indivi Percent  
This result proves that the distribution of the species at the  
two observation sites were different. Site I had the deepest  
zoning in the mangrove formation with a slightly hard substrate.  
Site II was located in the middle zonation closer to the outer area  
and contained muddy substrate. Anchor root plants  
No Family  
Gastropoda  
Species  
dual  
(%)  
Telescopium  
(Rhizopora sp.) dominated the location. The 10 species of  
1
Potamididae  
telescopium,  
1550  
85,92  
Mollusca were identified in the observation sites and only 2  
species, i.e., Telescopium telescopium and Nerita articulate,  
could be found at both the observation sites.  
The study revealed that the evenness of Mollusca in Kaisu  
mangrove area is low due to the identified of 10 species of  
mollusks but the presence of only 2 species (20%) at the two  
observation sites. This shows the adaptive advantage  
of Telescopium telescopium and Nerita articulate as compared  
to other species in Kaisu mangrove area. It is observed that  
mangrove vegetation Rhizophora influences the evenness of  
Linnaeus, 1758  
Steno melania,  
Fischer, 1885  
Neritaarticulat,  
Linnaeus, 1758  
Ellobiumaurisjudae,  
Roding, 1798  
Cheritideaobtusa,  
Lamarck, 1822  
Indothaisgradata,  
Jonas, 1849  
Sphaerassimineamin  
iata  
2
3
4
5
6
7
8
Thiaridae  
100  
55  
51  
23  
7
5,54  
3,05  
2,83  
1,27  
0,39  
0,22  
0,11  
Neritidae  
Ellobiidae  
Potamididae  
Muricidae  
Assimineidae  
Littorinidae  
Mollusca  
in  
the  
study  
site  
along  
with Sonneratia sp, Avicennia sp  
and Bruguera  
4
gymnorhiza, which are considered as a source of organic  
material and habitat for molluscs. Also, the condition of mud  
substrate which dominated Kaisu mangrove forest area became a  
factor that affected the presence of Mollusca in this forest.  
Nurrudin, Hamidah, & Kartika (31) observed out that the  
characteristics of the habitat and environmental conditions such  
as temperature, pH, salinity and types of substrate greatly  
influence the presence of Mollusca besides the condition of the  
mud substrate. They are among the dominant group in  
structuring the mangrove ecosystem and also constitute a  
component of fouling communities (32). Bivalve and gastropod  
are considered as the main molluscs of mangrove forests and  
comprise an important trophic component of detritus-based food  
webs. Gastropods have high distribution in the mangrove forests  
probably due to their mobile characteristic, while bivalves are  
often confined to a narrow seaward zone, due to feeding, larval  
settlement restrictions and sediment texture such as low pH and  
high organic matter (33).  
Littorariamelanosto  
ma, Gray, 1839  
2
Bivalvia  
Geloinaexpansa,  
Mousson, 1849  
Anumalocardisqua  
masa, Linnaeus,  
9
Corbiculoidea  
10  
0,55  
1
0
Veneridae  
2
0,11  
100  
1
758  
Amount  
1804  
Table 2: Composition of Mollusca by Site  
Individual  
Site I  
Telescopium telescopium, Linnaeus, 1758 1500  
No Species  
Site II  
50  
1
2
3
4
5
6
7
8
9
1
Steno melania, Fischer, 1885  
Neritaarticulata, Linnaeus, 1758  
Ellobiumaurisjudae, Roding, 1798  
Cheritideaobtusa, Lamarck, 1822  
Indothaisgradata, Jonas, 1849  
Sphaerassimineaminiata  
100  
30  
51  
25  
23  
7
4
Discussion  
The data presented in Table 1 revealed that composition of  
4
the Mollusca in Kaisu mangrove forest was less compared to the  
study by in the vicinity of TPI Parit 7, Tungkal I Village,  
Tanjung Jabung Barat, which found 15 species(31). Similarly,  
other studies have identified 33 species of gastropods in the  
mangrove ecosystem in the Gugus Pari Island, 19 species of  
gastropods in the Cilacap mangrove ecosystem, 16 species of  
gastropods in the mangrove forests of TelukAwurJepara, 29  
species of gastropods in the mangrove forest area of Segara  
Anakan Cilacap,14 species of Gastropods and 5 species of  
Bivalves in Aceh Besar, and 14 families of molluscs comprising  
Littorariamelanostoma, Gray, 1839  
Geloinaexpansa, Mousson, 1849  
Anumalocardisquamasa, Linnaeus, 1758  
Amount  
2
10  
2
1697  
0
107  
Note: Site I: mud substrate (land / mid zone),  
Site II: Mud substrate with sand (mid zone and sea)  
1
1 gastropod families (21 species) and bivalve families (3 types)  
in North Sulawesi (34), (35), (36), (37), (38). The detection of  
many species of gastropods found in these studies was due to the  
wider research location and longer sampling time. In  
comparison, the location of the present research was not large,  
and the sampling time was limited. All the identified species in  
our study were inhabitants of the mangroves as detailed below.  
Telescopium telescopium, Linnaeus, 1758. Telescopium  
telescopium belonged to gastropod group and accounted for  
the highest number of individuals in the study sites. It lives  
Figure 1: Domination index (C), diversity index (H) and evenness index  
e) of Mollusca in Kaisu mangrove forest  
(
1
178  
Journal of Environmental Treatment Techniques  
2020, Volume 3, Issue 3, Pages: 1176-1181  
in mangroves and could be found on mangrove floors with  
brackish condition (39).  
<H <3) and low if species diversity index was less than one (H  
<1). Based on these criteria, the diversity of Mollusca species in  
Kaisu mangrove forest area was considered low.  
Steno melania, Fischer, 1885. Steno melania accounted for  
the second-largest number of individuals. This species  
inhabited mangrove forests in both waterlogged and dry  
mud substrate with limited distribution and could be found  
only in site II.  
Analysis of species evenness level shows that value of  
evenness index of Mollusca species in Kaisu mangrove forest  
was 0.32, in which site I was 0.45 and site II was 0.21. (Krebs,  
1978) in (Odum, 1993) stated that the evenness value was  
considered high when e ≥ 0.6, moderate when e = 0.4 <e ≤0.6  
and low when e = 0 <e ≤ 0.4. Based on the criteria, the evenness  
index of Mollusca in Kaisu mangrove forest was low, including  
at site I and site II. The value of species evenness index,  
according to, ranged from 0 to 1 (46), (47). According to  
Santosa (48) amd Sinery (30), the evenness index of species  
indicated the size or proportion of individuals of each species in  
a community. If each species had similar number of individuals,  
then the community had maximum value of evenness index,  
which is the relative abundance of species (47). It is high if all  
species have similar distribution (i.e., similar population  
density)(49).  
Neritaarticulata,  
Linnaeus,  
1758.  
Neritaarticulata  
accounted for the third-largest number of individuals of the  
gastropod species. The species was found on mud  
substrates and fairly distributed on the location.  
Ellobiumaurisjudae, Roding, 1798. Ellobiumaurisjudae  
accounted for the fourth-largest gastropoda individuals  
found in the study site. This species was found on the mud  
substrate and documented only at site I.  
Cheritideaobtusa, Lamarck, 1822. This gastropod species  
was found on muddy substrates and only at the site II.  
According to, Cerithideaobtusa is commonly found in roots  
and stems of mangroves as well as mud substrates across  
the Asia-Pacific (21), (40).  
Indothaisgradata, Jonas, 1849. Indhothaisgradata species  
of gastropod was found only at site II. They inhabit both  
hard and soft substrata and were found on muddy substrates  
5 Conclusions  
The study concludes based on the result of the  
analysispresence of 10 species with 1804 individuals consisting  
of 8 species of gastropda (Telescopium telescopium, Steno  
melani, Nerita articulate, Ellobiumaurisjudae, Cheritidea obtuse,  
(41).  
Spherassimineamimata. Spherassimineamimata gastropod  
species were documented only at site I. Only a few  
individuals of this species were found on a muddy  
substrate.  
Indothais  
gradate,  
Spherassimineamimata,  
Littorariamelanostoma) and 2 species bivalvia (Geloinaexpansa,  
Anumalocardisquamasa) in the Kaisu mangrove forest area of  
Bongga District, Sarmi Regency. The dominance index of the  
identified Mollusca in Kaisu area was 0.74, with dominance of  
Telescopium telescopium with the species diversity index of  
Littorariamelanostoma, Littorariamelanostoma was  
a
species of gastropod recorded only at site II. A few  
individuals of thespecies was found on muddy substrate.  
They survived on mangrove leaves and brown algae as food  
sources, with significant differences among the three  
mangrove forests, and showed significant seasonal  
variation in its diet (42).  
0
.27 (low category) and species evenness index of 0.32 (low  
category).  
Acknowledgements  
Geloinaexpansa, Mousson, 1849. Geloinaexpansa belonged  
to Bivalvia group and was documented only at site I. The  
clams, known locally as Omapoko or Siini and Kawe or  
Kae, are used as protein source by local people and the  
species was found on muddy habitat as well as other  
species (43).  
The authors are thankful for Snowice Baransano and local  
community in Kaisu Village and Environmental Research  
Center of Papua University for their assistance and contribution  
during field data collection. A special thanks is also extended to  
those who have contributed to the research and wrote this article.  
Anumalocardisquamasa,  
Linnaeus,  
1758.  
Competing interests  
The authors declare that there is no conflict of interest that  
would prejudice the impartiality of this scientific work.  
Anumalocardisquamasa belonged to Bivalvia group and  
was found only at site I. This species was found on muddy  
habitat with limited number of individuals. They are  
widespread species which reside in 2-4 cm depth stratum  
Authors’ contribution  
All authors of this study have a complete contribution for  
data collection, data analyses and manuscript writing  
(44), (45).  
Fig.1 presents that the dominance index of the Mollusca  
species in Kaisu mangrove was 0.74 (close to 1). This indicated  
the dominance of certain species, especially Telescopium  
telescopium, particularly in site II, as there was no apparent  
dominance of certain species in site I. The criteria for dominance  
index according to were 0 <C <0.5 = there was no dominant  
species; 0.5> C> 1 = There were dominant species(23). The  
result shows that diversity index of Mollusca in Kaisu mangrove  
forest was 0.27. Observation also indicated species diversity of  
site II was higher than site I; however, diversity at both sites was  
considered in the low category. Species diversity was considered  
high if the species diversity index was more than three (H≥3),  
medium if species diversity index was between one to three (1  
References  
1. Angrianto R, Peday H. Z, Rahawarin Y. Y, Lekitoo K, Paiki  
T and Sinery A. S. Revetation of mangrove area aftaer  
exploration based Indigenous community. Yogyakarta:  
Deepublish, 2018.  
2
.
Prabhakar P. R. Molluscan diversity in mangrove ecosystem  
of Uran (Raigad), Navi Mumbai, Maharashtra, West coast of  
India. Bulletin Environment Pharmacology Life Sciences.  
2
012;1(6):55-59.  
1
179  
Journal of Environmental Treatment Techniques  
2020, Volume 3, Issue 3, Pages: 1176-1181  
3
.
Berger U, Rivera-Monroy V. H, Doyle T. W, Dahdouh-  
Guebas F, Duke N. C, Fontalvo-Herazo M. L, H.,  
Hildenbrandt N. Koedam, Mehlig U, Piou C and Twilley R.  
R. Advances and limitations of individual-based models to  
analyze and predict dynamics of mangrove forests: a review.  
Aquat Bot. 2008;89:260-274.  
17. Christensen S. M, Tarp P and Hjortsø C. N. Mangrove forest  
management planning in coastal buffer and conservation  
zones, Vietnam:  
a
multimethodological approach  
incorporating multiple stakeholders. Ocean  
Management. 2008;51:712-726.  
& Coastal  
1
1
2
8. Jutting B. Systematic studies on the non-marine molusca of  
the Indo-Australian archipelago. Trubia. 1956;28(2):259-  
477.  
4
5
.
.
Murdiyarso D, Purbopuspito J, Kauffman J. B, Warren M.  
W, Sasmito S. D, Donato D. C, Manuri S, Krisnawati H,  
Taberima S and Kurnianto S. The potential of Indonesian  
mangrove forests for global climate change mitigation.  
Natural Climate Change. 2015 Jul 1;5(12): 1089-1092.  
9. Poutiers J. M. The living marine resources of the western  
central Pacific. FAO Species Identification Guide for  
Fishery Purposes. 1998;1(4):363-648.  
Clüsener-Godt M and Cárdenas Tomažič M. R. The  
Importance of mangrove ecosystems for nature protection  
and food productivity: actions of UNESCO’s man and the  
biosphere programme. in Halophytes for Food Security in  
Dry Lands, M. A. Khan, M. Ozturk, B. Gul and M. Z.  
Ahmed. Eds. Academic Press. 2016:125-140.  
0. Houbrick R. S. Systematic review and functional  
morphology of the mangrove snails Terebralia and  
Telescopium (Potamididae; Prosobranchia). Malacologia.  
1
991;33(1-2):289-338.  
2
2
1. Karyanto P and Hadisusanto S. Animal ecology learning: the  
diversity pattern of gastropoda community in Cilacap  
mangrove ecosystem. Bioedukasi. 2004;2(1):23-28.  
6
.
Balasuriya A. Coastal area management: biodiversity and  
ecological sustainability in Sri Lankan perspective. in  
Biodiversity and Climate Change Adaptation in Tropical  
Islands, C. Sivaperuman, A. Velmurugan, A. K. Singh and I.  
Jaisankar. Eds. Academic Press. 2018:701-724.  
2. Simpson E. H. Measurement of diversity. London: Nature,  
1
949.  
23. Odum E. P. Fundamentals ecology. 3 ed. Yogyakarta:  
Gadjah Mada University Press, 1993.  
7
8
.
.
Prié V. Molluscs. in Encyclopedia of Caves. 3 ed. W. B.  
White, D. C. Culver and T. Pipan. Eds. Academic Press.  
24. Odum E. P. Fundamental Ecology. Philadelphia: W.B.  
Sounders Company, 1971.  
2
019:725-731.  
Pyron M and Brown K. M. Introduction to mollusca and the  
class gastropoda. in Thorp and Covich's Freshwater  
Invertebrates: Ecology and General Biology. 4 ed. J. H.  
Thorp and D. C. Rogers. Eds. Academic Press. 2015:383-  
25. Cappenberg H and Panggabean M. G. Mollusca in coral  
waters of Pari island cluster, Seribu islands, Jakarta bay.  
Jurnal Oseanologi dan Limnologi di Indonesia.  
2005;37(1):69-80.  
4
21.  
2
6. Magurran A. E. Ecological diversity and measurement. New  
Jersey: Princetown University Press, 1988.  
9
1
.
Brusca R. C and Brusca G. j. Invertebrates. Sunderland,  
Massachusett: Sinaeur Association Inc Publishing, 1990.  
2
7. Pielou E. C. The measurement of diversity in different types  
of biological collections. Journal of Theoretical Biology.  
1966;13:131-144.  
0. Corbeil S and Berthe F. C. Disease and mollusc quality. in  
Shellfish Safety and Quality, S. E. Shumway and G. E.  
Rodrick. Eds. Woodhead Publishing. 2009:270-294.  
2
8. Bratawinata A. A. Ecology of tropical forest and forest  
analysis method. Forestry Faculty of Mulawarman  
University, Samarinda; 1988.  
1
1. Kristensen E, Bouillon S, Dittmar T and Marchand C.  
Organic carbon dynamics in mangrove ecosystems: a  
review. Aquat Bot. 2008;89:201219.  
2
3
3
9. Krebs C. J. Experimental analysis of distribution of  
abudance. New York: Haper & Row Publisher, 1985.  
1
1
1
2. Pramudji. The mangrove forest ekosystem and its role as  
habitat for various aquatic fauna. Oseana. 2001;26(4):13-23.  
0. Sinery. The management strategy of Cuscus at Numfor  
Island. Yogyakarta: Deepublish, 2015.  
3. Haszprunar G and Wanninger A. Molluscs. Current Biology.  
2
012;22(13):R510-R514.  
1. Nurrudin, Hamidah A and Kartika W. A. The diversity of  
gastropods species around Parit fish auction, Tungkal I  
Village, West Tanjung Jabung. Biospecies. 2015  
Jul;8(2):51-60.  
4. Rusnaningsih. The community Structure of Gastropoda and  
population study of Cerithidea Obtusa (Lamarck 1822) in  
Pangkal Babu mangrove forest Tanjung Jabung Barat  
Regency, Jambi. MIPA Faculty, Indonesia University:  
Jakarta, 2012.  
3
3
2. Mohanjaru R. Macrofaunal assemblages of carbyn’s cove  
mangroves, South Andaman. in Marine Faunal Diversity in  
India, K. Venkataraman and C. Sivaperuman. Eds.  
Academic Press. 2015:473-483.  
1
1
5. Taberima S, Nugroho Y. D and Murdiyarso D. The  
distribution of carbon stock in Selected mangrove ecosystem  
of wetlands Papua: Bintuni, Teminabuan, and Timika  
Eastern Indonesia. in International Conference on Chemical,  
Environment & Biological Sciences (CEBS-2014). Kuala  
Lumpur. 2014.  
3. Kabir M, Abolfathi M, Hajimoradloo A, Zahedi S,  
Kathiresan  
K and Goli S. Effect of mangroves on  
distribution, diversity and abundance of molluscs in  
mangrove ecosystem: a review. Aquaculture, Aquarium,  
Conservation & Legislation International Journal of the  
Bioflux Society. 2014;7(4):286-300.  
6. Kathiresan K and Rajendran N. Coastal mangrove forests  
mitigated tsunami. Estuarine, Coastal and Shelf Science.  
2
005;65:601-606.  
3
4. Ayunda R. The structure community of gastropoda at  
mangrove ecosystem in Gugus Pulai Pari island group,  
1
180  
Journal of Environmental Treatment Techniques  
2020, Volume 3, Issue 3, Pages: 1176-1181  
Kepulauan Seribu. Indonesia University, Depok; 2011.  
Carolina; 2008.  
3
5. Silaen I. S, Hendrarto B and Supardjo M. N. Distribution  
and abudance of gastropoda in Awur Bay of Jepara  
Mangrove Forest. Journal of Management of Aquatic  
Resources. 2013;2(3):93-103.  
Author Profile  
Dr. Jacob Manusawai, was born in Sorong  
on October 6, 1958. Completed a Bachelor  
in forest management study program at  
Universitas Cendrawash in 1986. In 2005 he  
completed his master of law at the Law  
Study Program Universitas Hasanuddin  
Makassar. In 2015 he completed his  
3
3
6. Pribadi R, Hartati R and Suryono C. A. Composition of type  
and ditribution of gastropod in the Segara Anakan Mangrove  
Forest area of Cilacap. Ilmu Kelautan. 2009 Jun;14(2):102-  
1
11.  
7. Irma D and Sofyatuddin K. Diversity of Gastropods and  
Bivalves in mangrove ecosystem rehabilitation areas in  
Aceh Besar and Banda Aceh districts, Indonesia.  
Forestry  
Doctorate  
at  
Universitas  
Mulawarman y Samarinda. Since 1989 he  
has worked as a teaching staff majoring in  
Forestry, Faculty of Agriculture, Universitas  
Cenderawasih (currently the Faculty of  
Forestry, University Papua, Manokwari).  
His main research on environemtal sciences.  
Aquaculture, Aquarium, Conservation  
Bioflux. 2012 May 15;5(2):55-59.  
&
Legislation  
3
3
8. Baderan D. W. K, Hamidun M. S, Utina R, Rahim S and  
Dali R. The abundance and diversity of Mollusks in  
mangrove ecosystem at coastal area of North Sulawesi,  
Indonesia. Biodiversitas. 2019 Apr;20(4):987-993.  
Dr. Anton Silas Sinery, S.Hut., MP., was  
Born in Waropen, Papua on January 27,  
1979. He received undergraduate, master,  
and doctoral degree all majoring forestry  
science in 2002, 2008, and 2013 and from  
Universitas Papuan and Universitas  
Mulawarman. Currently he is a lecturer at  
Department of Environmetal Science  
Universitas Papua. His main research in  
environmental science.  
9. Kurniawati A, Bengen D. G and Maddupa H. Mangrove  
swamp condition and telescopium telescopium density in  
Segara Anakan lagoon, Cilacap Regency. Oseanologi dan  
Limnologi di Indonesia. 2014 Aug 2;40(2):221-234.  
4
4
0. Cahyani R. T. Study of bioactive components activity of  
Cerithidea Obtusa. Bogor Agricultural Institute, Bogor;  
2
015.  
1. Proum S, Santos J. H, Lim L. H and Marshall D. J. Metal  
accumulation in the tissues and shells of Indothais gradata  
snails inhabiting soft and hard substrata in an acidified  
tropical estuary (Brunei, South East Asia). Regional Studies  
in Marine Science. 2016 Nov;8(3):487-497.  
Rina N. Jowey, was born in Jayapura on  
March 5, 1986. Completed  
a Bachelor  
degree majoring Forestry in the Forest  
Cultivation study program at the Faculty of  
Forestry, Universitas Papua (2008). In 2014  
he completed his Masters degree in Forest  
Management at Michigan State USA. Since  
4
2. Chen L, Yan T, Xiong Y, Zhang Y and Lin G. Food sources  
of dominant macrozoobenthos between native and non-  
native mangrove forests: A comparative study. Estuarine,  
Coastal, and Shelf Science. 2017 Mar;187:160-167.  
2
008 he has worked as a teaching staff  
majoring in Forestry at the Faculty of  
Forestry, Universitas Papua, Manokwari.  
4
4
3. Dwiono S. A. Introduction to mangrove clams, Geloina  
Erosa and Geloina Expansa. Oseana. 2003;XXVIII(2):31-38.  
4. Roopnarine P. D, Signorelli J and Laumer C. Systematic,  
biogeographic and microhabitat-baseed morphometric  
variation of the bivalve anomalocardia squamosa (bivalvia:  
veneridae: chioninae) in Thailand. The Raffles Bulletin of  
Zoology. 2008;18:95-102.  
4
5. Lee S. S. Distribution pattern and interaction of two infaunal  
bivalves, Tapes philippinarum (Adams and Reeve) and  
Anomalocardia squamosa (Linnaeus) (Bivalvia: Veneridae).  
Journal of Experimental Marine Biology and Ecology. 1996  
Sep;201(1-2):253-273.  
4
4
6. Krebs C. J. Ecological methodology. New York: Harper &  
Row Inc Publisher, 1989.  
7. Sugianto. Quantitative ecology: Analysis methods of  
population and community. Surabaya: Usaha Nasional,  
1
994.  
4
4
8. Santosa Y. Wildlife diversity measurement techniques.  
Department. Bogor Agricultural University, Bogor; 1995.  
9. Baker V and Savage R. Development of a wetland  
monitoring program for headwater wetlands in North  
Carolina. NC Division of Water Quality, Raleigh, North  
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