used as bioindicators of pollution because they
feed on detritus and more abundant where the
environmental has better conditions. Economi-
caly, gastropods are consumed as food, and the
shells are used as an industrial raw materials for
accessories, necklaces and tapestries, as well as
being consumed by other gastropods (Paror-
rongan et al. 2018).
Previous research related to the diversity of
intertidal organisms in Tolitoli Regency has been
carried out on starfish in Bajugan beach (Putri
and Potoboba 2022) and on gastropods in the vil-
lage of Binontoan (Yanti et al. 2022). Coastal
areas with abundant gastropods can be found in
the Tolitoli district, Central Sulawesi. Kapas
Island is a distinctive marine area for tourism,
where gastropods are extensively harvested for
local consumption and as economic support for
inhabitants (BPS 2017). Overexploitation is a
possible consequence of uncontrolled extractive
activities in the island (Parorrongan et al. 2018).
Based on this information, diversity and abun-
dance become one of the benchmarks for assess-
ing the sustainability of marine ecosystems. In
order to determine the status of these aquatic
organisms, the diversity and abundance of gas-
tropods in Kapas Island were evaluated.
This research was conducted for two months
off the coast of Kapas Island, Tolitoli Regency,
Central Sulawesi Province, Indonesia (1° 16' 58"
N-120° 47'57"E). Gastropods were collected at
10 sampling stations (Figure 1). For each station,
three transect lines of 50 m and 150 m in width
were established towards the sea, perpendicular
to the shoreline, divided into three levels, namely
upper, middle, and lower intertidal. The distance
between stations was ∼150 m. A total number of
90 plots (quadrats) of 1 ×1 m were randomly
selected (English et al. 1997). Gastropods found
in each plot were identified, sorted and num-
bered, and three individuals for each species were
preserved in formalin 70% (Rukmana and
Purnomo 2019). All specimens were deposited at
the Madako Tolitoli University Laboratory. Envi-
ronmental observations included the substrate
type and in situ water temperature and pH.
Gastropods were identified to the lowest taxo-
nomic level using identification books (Dharma
1988) and journals (Bula et al. 2017; Haumahu
and Uneputty 2018; Rukmana and Purnomo
2019; Liline et al. 2021) based on morphological
characteristics such as shape, color, and shell. The
validity of species names was also checked from
the World Register of Marine Species (WoRMS)
database.
Frequency of incidence (FoI) was estimated
using the equation:
FoI = Ni.St ×100
N.St
where, Ni.St is the total number of locations
where the species iwas found, N.St is the total
number of sampling locations (Romimohtarto
and Juawana 2001). Frequency value ranges are
0-25% (very rare), 25-50% (rare), 50-75% (mod-
erate), and > 75% (frequent/absolute). Gastropod
abundance was calculated using the formula:
Ki = ni
A
where Ki is the individual abundance (density)
(ind. m-2), ni is the number of each species (indi-
vidual), and Ais the transect area (m2). The cal-
culation of gastropod diversity was done using
the Shannon-Wiener diversity index (H’):
H’ =-∑ Pi (LNPi)
where Pi is the proportion of the ith species, and
LN represent the logarithm of Pi. The Shannon-
Wiener diversity index is classified into three lev-
els: H’ <1 (low species diversity), 1 ≤H’ ≤3
(medium species diversity), and H’ >3 (high
species diversity) (Brower et al. 1990).
102 MARINE AND FISHERY SCIENCES 36 (1): 101-108 (2023)