Big defensins and mytimacins, new AMP families of the Mediterranean mussel Mytilus galloprovincialis
Exploitation and Management of Brown Mussel (Modiolus philippinarum) Resources in Iloilo,...
Transcript of Exploitation and Management of Brown Mussel (Modiolus philippinarum) Resources in Iloilo,...
Philippine Journal of Social Sciences and Humanities University of the Philippines Visayas Volume 16 No. 2, (2011) 22-34
-------------- * For correspondence email: [email protected]
Copyright © 2011 Napata, RP & Andalecio, MN
22
Original Research
Exploitation and Management of Brown Mussel (Modiolus philippinarum)
Resources in Iloilo, Philippines
Ruby P. Napata* and Merlina N. Andalecio
Institute of Fisheries Policy and Development Studies
College of Fisheries and Ocean Sciences
University of the Philippines Visayas, Miagao, Iloilo
Abstract
This study examined the status of the brown mussel (Modulus phillipinarium) resources in
Dumangas, Iloilo. The coastal area of Dumangas has been known for the production of brown
mussels, but stock management has been hampered by lack of information on its exploitation.
A face to face survey interview was conducted to determine the characteristics of gatherers,
harvesting methods, production data, and perceptions on the management and conservation of
the brown mussel resources. A total of 34 gatherers, between 24 to 67 years old ( =40 + 10.3
years old), were interviewed. Involvement in this small-scale industry was not limited to male
fishers, even women and children were involved. The respondents have been harvesting
brown mussels for an average period of 9.2 + 9.5 years. Gathering was done throughout the
year, typically once a day at three hours a day and six days a week. The methods utilized were
handpicking and diving in deeper waters. The average volume of brown mussels harvested
was 43.0 + 26.2 kg per gatherer per day. This study revealed that the volume of commercial
harvest was 74% more than small-scale harvest. The estimated price of PhP3.80/kg is very
much lower than the recorded price of green mussels. Harvesting of brown mussels for food
on a subsistence basis is common in Dumangas, but they have also been used as cheap source
of aquaculture feeds. Respondents were aware of the negative consequences of resource
depletion and recommended implementation of regulatory measures including size limit,
maximum volume of harvest, and frequency of harvesting. This study found the need to enact
a municipal-wide ordinance relating to the management and conservation of brown mussel
resources. The ordinance should provide for the establishment of brown mussel conservation
zone and creation of a management body.
.
Keywords: Modiolus philippinarium, brown mussel, shellfish harvesting, Dumangas, Iloilo
In recent years, increasing global interest on
the sustainable management of marine resources
focuses on the implementation of development
policies and programs in line with precautionary
principle, adaptive management, and ecosystem-
based management. This is to veer away from the
common property problems in fisheries such as
excessive fishing fleets and effort, overexploited fish
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stocks, by-catch, unprofitability and low incomes,
low contribution to national economy, threat to the
sustainability of the fishery, and human habitation
(Arnason, 2009; Pomeroy et al., 2007; Bhat & Bhatta,
2006). According to Cole, McQuaid & Nakin (2011),
habitat destruction is not necessarily a direct
alteration of environmental conditions, but loss of
biogenic habitat and subsequent alteration of habitat
structure and abiotic conditions. To address these
concerns, management measures then become
imperative and have been widely applied. These
include area and seasonal closure, establishment of
marine protected areas and fishery reserves, habitat
restoration, and community-based governance
approaches (Wiber et al., 2010; McLaughlin, Portig &
Johnson, 2007). The effects of management are
varied across spatial and temporal scales.
Among the most important aquatic resources
in the world are molluscs. In 2008, the global
production of molluscs, which reached 13.1 million
tons, was composed of 31.8% oysters, 24.6% clams,
12.4% mussels, and 10.7% scallops (FAO, 2010).
Molluscs are mostly found in rocky and intertidal
communities, yet many of them have been subjected
to intense exploitation by coastal communities.
Previous studies have shown that intertidal molluscs
are the main target taxa for small-scale fishers (e.g.,
Jimenez et al., 2011; Colonese et al., 2011; Szabó &
Amesbury, 2011). Bivalves such as oysters, mussels,
and scallops belong to the family of molluscs.
Compared to finfishes, which are highly mobile,
bivalves are sedentary in nature and lack a well-
defined defence mechanism against predators,
especially humans, which make them more prone to
overharvesting. Of the very few bivalve species and
despite commercial significance, mussel receives very
little attention in terms of conservation and
management. Mussels make up the hard bottom
communities in coastal waters, often forming
extensive biomass accumulations on rocks, jetty piers,
and navigation buoys (Rajagopal et al., 2006). Several studies have indicated ecological services of
mussels such as ecosystem engineers or habitat
forming species (Cole, McQuaid & Nakin, 2011;
Borthagaray & Carranza, 2007; Cranfield et al.,
2003), responsible for removing large phytoplankton
biomass and wastes as well as cycling of nutrients
(Strogyloudi et al., 2006; Gao et al., 2008; Peterson &
Heck, 1999).
In the Philippines, mussels are cheap sources
of animal protein. Although many species are
reported globally, only three species of mussel are
being utilized as food in the country, namely, Perna
viridis (green mussel), Modiolus metcalfei and
Modiolus philippinarum (brown mussels). The green
mussel is the only species farmed commercially, and
its significant volume of production is sustained
entirely by the abundance of wild seeds as there are
no commercial hatchery facilities in the country.
Conversely, the two species of brown mussels are not
suitable for farming because they are not known to
attach on substrates other than living adults growing
in dense mats on muddy bottoms (FAO, 1988; Yap,
1978). From 2004 to 2013, green mussels contribute
annual landings of 19,936.50 to 22,442.71 mt (BAS,
2012), whereas no production statistics are available
for brown mussels.
Many species of brown mussel of the genus
Modiolus are mostly found in the Indo-Pacific
Region, specifically, at the intertidal and very
exposed shores where they can form extensive beds.
More information on various species of Modiolus is
available in other areas. For example, findings on the
impacts of fishing, heavy metal pollution,
biodeposition, and energy budget of Modiolus
modiolus have been discussed by Magorrian &
Service (1998), Kenchington et al., (2007), Kavun &
Podgurskaya (2009), and Navarro & Thompson
(1997). Whereas, Barile et al., (2011), Ezgeta-Balic et
al., (2011) and Lesser & Kruse (2004) have examined
artificial reproduction technology and energy budget
of Modiolus barbatus. Information on the toxicity of
heavy metals on Modiolus philippinarium have been
established by Rajagopal et al. (2006) and
Ramakritinan, Rathishri, & Kumaraguru (2012).
Brown mussels are also the preferred food of cultured
species like prawns (Penaeus monodon) and mudcrab
(Scylla serrata) (Rochanaburanon, 1980). Despite
their ecological importance, the literature on
Modiolus in the Philippines is scarce. The limited
information available on their distribution, biology,
and settlement are found in Tumanda et al. (1997) and
Yap (1978). Also, the extent of exploitation and
effects of harvesting are poorly documented, but
ongoing anthropogenic activities in the coastal areas
may indicate steady exploitation that threatens
resource recovery. Thus, in order to recommend
appropriate management measures, this study
examined the status of the brown mussel resources in
one of the coastal areas in the province of Iloilo.
In Iloilo, two areas are known for the
production of brown mussels, and these are Banate
Bay and Dumangas. However, no studies were
conducted on the exploitation and management of the
brown mussel in both areas. An assessment of the
effects of exploitation has been hindered by lack of
data on natural fluctuations of stocks. The only
available information from Banate bay was the brown
mussel’s settlement preference. The municipality of
Anilao which is situated in the bay regulated the
collection in an attempt to prevent overharvesting that
may ultimately lead to species disappearance. In
Dumangas, baseline information is also very
inadequate. Based from historical accounts, the
gathering of brown mussels in Dumangas has been
practiced as early as the 1970s. With increasing
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aquaculture demand, brown mussels were used as
feeds for cultured mudcrabs.
Methodology
Study Site
This study was conducted in the
municipality of Dumangas, which lies 122°42’34”
longitude and 10°49’22” latitude, and has a total
coastline of about 21.6 km (Figure 1). Aside from
several creeks and springs, seven major rivers which
traverse the municipality provide the residents of the
locality with important fisheries resources. The
coastal area has extensive seagrass beds estimated to
be about 450 to 750 ha along 1.5-2 km shoreline at a
depth of 3-5 m, and diverse species of mangroves
(CRM Plan, 2009). Several man-made structures were
established on the coast namely, fishpens, cages,
oyster and mussel farms, and fish traps. Various
species of finfish and shellfish are caught in the
coastal waters including, slipmouths, croakers,
siganids, mackerels, groupers, nemepterids, crabs,
and shrimps. Of the shellfish fishery, mollusc is an
important group which has been exploited in great
volume from the intertidal areas, riverbanks,
mangroves and seagrass beds. The southern side of
the coastal area has been regarded as rich in mussel
resources.
Data Collection and Analysis
A face to face survey interview was
conducted using a pre-tested questionnaire which was
translated to the local language Ilonggo. The survey
questionnaire included socio-demographic profile,
harvesting methods, production data, and perceptions
on the management and conservation of the brown
mussel resources. The interviews were conducted
from August to November 2007 in six coastal
barangays namely, Bacay, Bolilao, Dacutan,
Lacturan, Paloc Sool and Sapao. Focus group
discussions with barangay captains, Barangay
Fisheries and Aquatic Resource Management
Councils (BFARMCs) chairpersons, and Agriculture
Technician for fisheries were also conducted to solicit
additional information and validate the information
collected from the interviews. The location of brown
mussel beds was identified from the interviews, and
the area covered was estimated using the Garmin 76
Mariner Global Positioning System (GPS). The
species of brown mussels were identified through the
assistance of Dr. Liberato Laureta of the Institute of
Aquaculture, College of Fisheries and Ocean
Sciences, University of the Philippines Visayas. The
primary data were supplemented with secondary
information such as municipal fisheries profile and
ordinances, memoranda of agreement, and technical
reports. Descriptive statistics was used to describe the
demographic characteristics of the respondents and
production data.
Figure 1. Location of Dumangas, Iloilo.
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Results
Profile of Brown Mussel Gatherers
The brown mussel beds in the municipality
of Dumangas were found in the 13.3-km stretch of
coastline covering an estimated area of 26.4 ha
(Figure 2). Mussel harvesting supports the livelihood
of about 150 gatherers from six barangays namely
Bacay, Lacturan, Dacutan, Sapao, Paloc Sool, and
Bolilao. A total of 34 respondents were interviewed,
representing 23% of the total brown mussel gatherers.
Their socio-demographic profile is shown in Table 1.
Most respondents were married males (70%), and
whose main sources of income were brown mussel
harvesting and fishing (Figure 3). The age of the
respondents ranged from 24 to 67 years old ( =40 +
10.3 years old). They have been involved in brown
mussel gathering from less than one year to 31 years
(( =9.2 + 9.5 years). For the respondents, engaging
in brown mussel harvesting has been an important
means to augment their family’s daily needs and
provide for their children’s education, especially for
those who have been in the business for 31 years. The
respondents who have been harvesting brown mussels
for over ten years were mostly from barangays Bacay
and Lacturan. Some who were new in the business
became gatherers only when the comprador or traders
entered the municipality and purchased huge
quantities of brown mussels.
Brown Mussel Species and Harvesting Methods
The species of brown mussel in the coastal
waters of Dumangas was identified as Modiolus
philippinarum. This species is known to attain sexual
maturity in three months, and spawns all year round.
Figure 4 shows M. philippinarum measuring between
1.0 to 1.25 inches that were sold to a comprador from
Capiz. These brown mussels were used as feeds for
high valued culture species like mudcrabs. The results
of the interviews revealed that brown mussels were
mostly harvested in barangays Paloc Sool, Bacay,
Sapao, and Dacutan. Family members were involved
in gathering, including women and children, either
individually or in groups. Each gatherer would
usually cover an average area of about 5 + 6.3 ha.
One respondent who was also a trader disclosed that
he contracted ten unlicensed gatherers to sell all their
harvests to him. Harvesting was done throughout the
year, with most respondents (74%) doing it once a
day (especially during low tide) at an average of three
hours a day and six days a week. The methods
utilized were handpicking or collection using bare
hands (74%) in the intertidal or shallow areas, and
diving (26%) in deeper waters. Small-scale gatherers
would select only big mussels (>2.5 inches) and in
small amount (e.g., one pail equivalent to 3-6 kg).
With diving method, brown mussels were harvested
in commercial quantity. Harvesting was done by
removing lumps of mussel from the substrate and
transferring them inside a rectangular collection box,
locally known as ‘ayagan.’ Ayagan, which measures
1.2m x 1.8 m, is made up of bamboo slats and plastic
containers as floaters (Figure 5). When the ayagan is
filled, the lumps of mussel are shaken thoroughly to
remove the mud and byssal threads. This process then
separates the mussels individually. The bamboo slats
were designed to allow the removal of debris, byssal
thread mass, and very small mussels. However, the
young mussels dislodged from the mats could have
been severely stressed with the removal of their
byssal threads, and are unlikely to survive when they
settle back to the substrate. This method of harvesting
may be considered non-selective and inefficient.
Also, when ‘ayagan’ is used, no sorting or size
selection is done compared to handpicking. Male
respondents mostly employed the diving method,
whereas women and children were into handpicking.
Brown mussel gatherers claimed that the growing
areas have become sparse or “patchy”, which may
indicate an overexploited condition contrary to what a
healthy mussel bed should look like i.e., forming a
dense mat.
Production Data
In this study, the total volume of production
was estimated with a degree of caution. Because the
distribution of mussel beds has become patchy, the
estimated daily and annual production data were
computed based on the quantity collected by
individual gatherers per unit time and not on the total
area gleaned. The volume of brown mussels harvested
was between 4.5 kg to 125.0 kg per gatherer per day,
averaging about 43.0 + 26.2 kg per gatherer per day.
The mean harvest by diving was 61.6 + 34.7 kg per
gatherer per day, whereas that of handpicking was
35.43 + 17.8 kg per gatherer per day. So with 150
gatherers and 6 days a week harvesting, the total
volume of mussels collected from the waters of the
Dumangas was estimated to be about 6.5 + 3.9 tons
daily, or 2,019 + 1,230 tons per year. Brown mussels
were sold fresh or processed. When sold fresh, they
can either be shell-on or without shell locally termed
as ‘tinala.’ Children ages 7 to 10 were also involved
in the activity called ‘tala’ (Figure 6). The average
selling price of shell-on was PhP190.8+107.8 per
sack (price range: PhP30-400 per sack) or PhP50 per
tray or pail. A sack and pail of brown mussels
weighed about 50 kg and 6 kg, respectively. Thus, the
estimated price of brown mussel was PhP3.80 + 2.20
per kg. The processed mussels called ‘ginamos’ were
sold at PhP25.00 per bottle. The female members of
the family mainly market brown mussels within
Dumangas, neighboring municipalities, and Roxas
City in the province of Capiz (Figure 7).
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Figure 2. Harvest areas of brown mussels in Dumangas.
Table 1. Demographic characteristics of the brown mussel gatherers in Dumangas. Characteristics Category All samples (N=34)
Gender Male 24
Female 10
Age (years) Mean 40
Maximum 24
Minimum 67
Marital status Married 33
Single 1
Location of residence of brown mussel gatherers
Bacay 9
Bolilao 1
Dacutan 9
Lacturan 10
Paloc-sool 2
Sapao 3
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Figure 3. Major and minor sources of income of brown mussel gatherers.
Figure 4. Brown mussel species collected from barangay Bacay.
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Figure 5. A rectangular collection box, locally known as ‘ayagan’, used in commercial harvesting of brown
mussels.
Figure 6. Children involved in harvesting activity called ‘tala’.
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Figure 7. Areas where brown mussels from Dumangas were marketed (multiple responses).
Management and Regulatory Aspects of Brown
Mussel Resources
More than half of the respondents (56%) had
paid the annual municipal permit (PhP150 to PhP260)
and barangay clearance (PhP20) allowing them to
harvest shellfish. In addition, they also paid the
required PhP5 for every sack of brown mussels
transported outside the municipality. However, those
who refused to pay the permits reasoned that brown
mussel is an open resource and anyone from
Dumangas should be allowed to collect it at no cost.
Most respondents (91%) indicated that they were not
receiving assistance from the government for the
brown mussel industry. Over 80% of the respondents
were knowledgeable of existing fishers organizations
such as Barangay Fisheries and Aquatic Resource
Management Councils (BFARMCs) and Dumangas
Federation of Fisherfolks, Inc. (DUFFI), but only
47% were members of these organizations. More than
half (62%) of the respondents were familiar with
regulations on the harvesting of brown mussels,
which include size limit (i.e., more than 1.5 inches
should be harvested), frequency of harvesting which
is three times a week, restricted to the residents of
Dumangas, and issuance of the required permit to
gather. Some respondents mentioned that they have
known about the harvest size restriction only from
other gatherers. The gatherers were also prohibited
from completely harvesting all stocks. According to
them, the officials and members of BFARMCs collect
the barangay tax, and would normally monitor the
area to deter encroachment by outsiders.
All respondents agreed that there is a need to
manage and conserve the brown mussel resources,
and they recommended that management should
focus on the following:
Setting size limits
Specific ordinance on brown mussel
harvesting
Delineation of the municipal waters of
Dumangas
Leaving at least 10% of spawner or adult
brown mussel
Presence of active law enforcement team
Strictly implementation of the regulation that
brown mussel is exclusively for the residents
of Dumangas
Limit on the volume of harvest (e.g., 1 sack
per person per day)
In Dumangas, there was no specific policy
exclusive to brown mussel resources, but the
information in Table 2, although insufficient, may
address some regulatory concerns. Because of
extensive collection and increasing volume of
harvest, the barangay officials of Bacay were
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prompted to formulate Ordinance No. 02-2006. The
ordinance imposes collectible tax and requires all
brown mussel gatherers and traders/buyers operating
in the coastal vicinity of the barangay to secure a
barangay clearance and Mayor’s permit. In addition,
the ordinance sets the following provisions:
Brown mussels found in the coastal vicinity
of barangay Bacay is for all Dumangasanon
only;
The barangay imposes PhP5.00 tax for every
sack of brown mussel, and a maximum of
two (2) sacks per gatherer;
The harvested brown mussel will be subject
for inspection by an authorized person from
the Barangay Council;
The allowable size for harvest should be two
(2) inches and above.
Table 2. Some policies of the municipality of Dumangas related on management and conservation of brown mussel
Classification Ordinance Provision
Permitting/Licensing Ordinance No.2004-01, Chapter IV, Section 19
Gives priority to resident municipal fisherfolk
Ordinance No.2004-01, Chapter IV, Section 17
There should be a registry of municipal fisherfolk and fish worker
Ordinance No.2004-01, Chapter VI, Section 34
No person, partnership, association, corporation, cooperative shall gather or culture oyster and mussel within the municipal waters without permit or license issued by the Mayor in accordance with the provision of this Ordinance
Ordinance No. 2005-22, Section 39E
Shell gathering with Mayor’s permit of PhP150.00.
Ordinance No. 2005-22, Section 39N
Registration fee for fisherfolk/fishworker of P5.00
Prohibitions on Illegal Activities
Ordinance No.2004-01 Chapter 5, Section 22.6
Protection of the marine environment and imposition of appropriate penalties for acts which endanger the environment, such as dynamite fishing and other activities, which result in population or ecological imbalance
Ordinance No.2004-01, Chapter X, Section 75
It is unlawful for any person or entity to collect, gather or sell scallop locally known as “tikab” less than five (5) inches measures from the hinge of the shell, and other mollusks or shelled-fishes which does not reached the maturity stage, or as may be determined by the national government and or accredited institutions
Protection/Conservation Measures
Ordinance No.2004-01, Chapter X, Section 45b
The vicinity of the Lapuz-lapuz islet in Brgy. Bacay and Paloc Sool containing an area of 89.134 hectares is designated as fish and marine sanctuary. The area is designated for the exclusive use of the government for the propagation, education, research and scientific purposes. It is hereby prohibited for any person to fish, extract/collect shells, seaweeds or conduct any form of activity such as boating, mooring, and various fishing techniques or other activities harmful to the ecosystem in the area.
Ordinance No.2004-01, Chapter X, Section 61
It shall be unlawful for any person, association or corporation to gather, collect, or kill marine life inside the marker where the marine sanctuary is established. That within the core of the fish sanctuary and breeding area, fishing or collection of marine life is not permitted.
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There were cases when the implementation
of the said Ordinance was challenged. One of these
transpired on September 2007 when the local
Philippine National Police (PNP) confiscated a truck
load of brown mussels in Bacay. In view of this, a
joint Memorandum of Agreement (MOA) was
formulated between the local government through the
Mayor, gatherers, traders and the barangay captain.
Based on interviews, the agreement contained the
following provisions: a) Gatherers may only harvest
brown mussel of mature and marketable size, ranging
from 1.5-2 inches; b) Harvesting may be be done on
Mondays, Wednesdays, Fridays, Saturdays, and
Sundays; c) Harvest is limited to no more than two
(2) sacks per person per day. In Lacturan, a MOA
was also signed between the barangay captain,
president of Brown Mussel “tahong” Hunters
Association and the local government. The agreement
included: a) Gatherers may only harvest brown
mussel of mature and marketable size, ranging from
1.5-2 inches; b) Harvesting may be done throughout
the week (Mondays to Sundays); c) Harvest is limited
to no more than one (1) sack per person per day.
Because Lacturan residents would also gather brown
mussels in front of Bacay, the municipality has
designated harvest areas for these two barangays so as
to avoid conflicts among gatherers. The barangays
were then expected to be responsible in managing the
brown mussel resources in their respective areas.
Discussion and Conclusion
The fishing communities of Dumangas have
been engaged in brown mussel harvesting for several
years now. Although the industry does not contribute
much to the local economy compared to other
fisheries and aquaculture industries (e.g., milkfish and
prawn culture), it is a secondary source of income for
fishers and their families. Involvement in this small-
scale industry was not limited to male fishers, even
women and children were involved. This situation is
similar to the studies of Frangoudes, Marugán-Pintos,
& Pascual-Fernández (2008), Aswani & Weiant
(2003), and Kyle, Robertson, & Birnie (1997), which
indicate that women and children are also actively
involved in shellfish harvesting. Harvesting of brown
mussels for food on a subsistence basis is common in
Dumangas, but they have also been used as cheap
sources of aquacultures feeds. The study of
Rochanaburanon (1980) has demonstrated that
marketable size and small brown mussels (Modulus
metcalfei) have higher protein content (71.49% and
67.10% dry weight, respectively) than the marketable
size green mussel (Perna viridis), 63.94%. This may
be comparable to the protein content of trash fish and
the highly expensive formulated feeds for finfish.
Although two species of brown mussels
were found in the Philippines, only Modulus
philippinarium was identified in Dumangas. Jimenez
et al. (2011) described harvesting of intertidal fauna
as an informal and opportunistic activity that is
difficult. Among the potential impacts they identified
include decreases of catch densities, trampling related
degradation of habitats, and changes in community
composition. In general, harvesting mussels from
their natural habitat involves cutting of byssus threads
(Rajagopal et al., 2005). Compared to other species of
mussels which when manually detached would
quickly produce byssus threads and re-attach to any
solid surface (Rajagopal et al., 2005), Modiolus once
removed from a living surface will unlikely to re-
attach themselves, and will eventually die. This
would mean that precautionary measures should be
considered during harvesting. Indiscriminate
harvesting may compromise the integrity and
recovery of seabed which according to Trigg &
Moore (2009) may be an important function of byssal
threads of bivalves. In this present study, the two
harvesting methods (i.e., hand picking and diving
using ‘ayagan’) have some disadvantages. Although
handpicking is small-scaled and more selective
because gatherers may only collect the prescribed size
of 1.5 to 2.0 inches, there is still a possibility that
when gatherers are not cautious in harvesting, this
would create disturbance that will have the potential
to cause physical changes to the mussel beds. This is
especially the case when children are involved. On
the other hand, the diving method is non-selective,
and therefore, even smaller mussels are being
collected.
It is believed that spawning of brown
mussels is throughout the year because spat can be
found in significant quantities in the environment.
Such availability could have resulted to more
commercial harvesting, as revealed in this study that
the volume of commercial harvest was 74% more
than small-scale harvest. Should the demand for
brown mussels from aquaculture continue to increase,
commercial harvesting will most likely intensify. The
presumed abundance in the wild could have also
lowered the market price of brown mussels. In fact,
the estimated price of PhP 3.80/kg is very much lower
than the PhP 14.5/kg price of green mussels in Iloilo
in 2010 (BAS, 2012). However, without baseline data
on price trend, this assumption requires further
validation.
The notion that a natural resource is infinite
and its use is not supposed to incur a corresponding
fee is still prevalent among coastal fishers. But
respondents who were aware of the negative
consequences of resource depletion opted for the
implementation of regulatory measures. Respondents
who recognized the need to set harvest size restriction
mentioned that too many gatherers have been
harvesting smaller sizes of brown mussels. Also,
there was no restriction on the number of brown
mussel gatherers. Harvest control regulations were
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only implemented in barangays Bacay and Lacturan
through Memoranda of Agreements. The salient
features of the agreements are size limit, maximum
volume of harvest, and frequency of harvesting.
There was no mention as to the basis for these
regulations. However, the size limit of 1.5-2.0 inches
is similar to the minimum length of 50 mm (or 2
inches) permitted for harvesting Modiolus barbatus in
the Mediterranean coast, which is attained on the
third year of life (Barile et al., 2011). The two
agreements have limitations because these are not
legally binding. But these can serve as bases for the
enactment of a municipal-wide ordinance relating to
the management and conservation of brown mussels,
as suggested by the respondents. The ordinance
should provide for the establishment of brown mussel
conservation zone and creation of a management
body. The management body shall be responsible in
the issuance of permits, prioritization of gatherers,
and law enforcement in the conservation zone.
Management strategies to be identified should be
based on stock assessment studies and detailed
surveys. These shall include among others, size limit,
frequency of harvest, permissible volume of harvest,
maximum number of gatherers at any given time, and
issuance of limited number of permits or licenses. If
the harvesting is whole year round, it may be
appropriate to designate closed season. Albeit the
municipality has not yet delineated its municipal
waters, this should not be an impediment in the
formulation of this ordinance. The recommendation
of the respondents to retain 10% spawners or mature
brown mussels may be conservative, and its
implication should be further examined. The findings
of this study provided a starting point from which
further management of brown mussel resources could
be done.
Acknowledgment
This study was conducted as part of the
CIDA-funded project “Principles in Practice (PIP):
Ocean and Coastal Governance in Vietnam and the
Philippines”. We would like to express our gratitude
to the following for their assistance in the conduct of
the study: Alan Dino Moscoso, Micah Espia and
Alvin Bandorio for their help during data collection;
Dr. Liberato Laureta, for his assistance in species
identification; local government officials especially
Marlene Amora; brown mussel gatherers from
barangays Bacay, Bolilao, Dacutan, Lacturan, Paloc
Sool and Sapao as my respondents; and Recardo
Mieux for his comments on the manuscript.
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