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International journal of Rural Development, Environment and Health Research (IJREH) [Vol-3, Issue-3, May-Jun, 2019]
https://dx.doi.org/10.22161/ijreh.3.3.5 ISSN: 2456-8678
www.aipublications.com/ijreh Page | 110
Catch Per Unit Effort (CPUE) of Bivalves in
Northwestern Bohol, Philippines
Margie P. Vito, MSc, Anthony S. Ilano,Ph.D.
Department of Biology, University of San Carlos, Talamban Campus, Cebu City
Abstractโ€” Catch Per Unit Effort (CPUE) is a measure of status of marine resource in a given area. In this study, bivalve fishery
information was gathered using the self-structured questionnaire. There were 61 respondents who were the registered fishermen
of Calape, Tubigon and Clarin. Among the three towns it was Clarin where highest mean CPUE was observed with
1.2kg/hr/man. This was followed by Calape with 0.8kg/hr/man and lowest mean CPUE was recorded in Tubigon with
0.6kg/hr/man. High CPUE value means that there are still enough bivalve resources in the area and lowest CPUE means that
these resources are endangered.Considering that,the result of this study showed that there is a need to regulate the collection of
bivalves with lower wild stocks to avoid loss of these natural resources.
Keywordsโ€” Collection, Gleaning Mangroves, Seagrass and Wild stocks.
I. INTRODUCTION
Bivalves community as part of benthic organisms is
considered as an efficient tool of marine fishery assessment.
They belonged to mollusks phyla which was considered as
the most abundant marine organisms (Subba Rao, 1993).
Bivalve species can be found all around the globe in variety
of environments, from the poles to the tropics. Over such
array, environmental conditions vary such as water
temperature, dissolved oxygen, salinity and potential
hydrogen. These differences influenced growth,
reproduction and survival but on the other hand, it limits
their distribution.
They are ecologically important since they served
as a bio indicator for water pollution. Although, they mostly
thrive in clean waters but some species would occur in
polluted waters (Medeiros, 1997). They are suspension
feeders and these feeding strategies pose different problems
with respect to threshold levels of environmental stress
(Calebrase et al., 1984). Economically, they areharvested
for food and livelihood resource. As a matter of fact, out of
total harvested aquatic resources, about 10% of annual food
was consumed through bivalve harvesting (Roberts, 1999).
They are also very important in shell industry.
In the Philippines, majority of the population live in coastal
areas with livelihood mostly involving fishing. Majority of
coastalhouseholds (53%) are engaged in subsistence fishing
particularly gleaning for invertebrates and small fishes.
Gleaning is almost a daily activity done during low tide 2-3
hours and is largely confined to sea grass beds, rocky reef
flats and occasionally along the edge of mangrove forests. It
involves men, women and children with various ages. Most
of the gleaners were engaged in this activity for 20-40 years
while few have been gleaning for 50 years. Engagement is
especially higher (60%โ€“72%) in remote fishing villages and
small islands with little access to other income sources (De
Guzman et al., 2014).
In this regard bivalves which are one of the highly
gleaned marine invertebrateswere under shade of
endangered species (Shainmugam and Vairamani, 2005).
Hence, this study is necessary to know the volume of
bivalves caught per gleaning operation in Northwestern,
Bohol to know the sustainability of these marine resource.
The bivalves were collected in three towns specifically,
Clarin, Tubigon and Calape comprising the Northwestern
part of the province. These towns constitute 90% of bivalve
fishing industry in Bohol because these are coastal
municipalities. This study is vital to know the present
condition of bivalves in the area.
II. OBJECTIVES OF THE STUDY
This study generally aimed to determine the catch per unit
effort of bivalves in the area. Specifically, it would compare
the catch per unit effort of bivalve species caught in each
town namely: Clarin, Tubigon and Calape. Species of
bivalves will also be noted as well as the income per unit
effort.
III. MATERIALS AND METHODS
The information on bivalve catch in Northwestern Bohol
Philippines was done by interview using the self-structured
survey questionnaire in (Appendix A). The respondents of
the study were the registered fishermen/gleaners in three
towns. A total of 61 individuals were the respondents of the
study. There were 21 respondents in Clarin, 20 in Tubigon
and 20 in Calape respectively. Aside from face-to face
interview, an actual field survey was also conducted.
Randomly selected fishermen were selected to glean in the
sampling area and they were timed fromthe start and end of
gleaning activity.
IV. DATA ANALYSIS
The Catch Per Unit Effort (CPUE) was determined
using the daily total catch data as total weight in kilograms
and daily fishing time spend for each collector. CPUE was
computed using the formula of Bantoto and Ilano (2012):
CPUE= Total weight of catch (kg)
Totalfishingtime/hr/collector(man)
Income Per Unit Effort (IPUE) was calculated using the
formula:
International journal of Rural Development, Environment and Health Research (IJREH) [Vol-3, Issue-3, May-Jun, 2019]
https://dx.doi.org/10.22161/ijreh.3.3.5 ISSN: 2456-8678
www.aipublications.com/ijreh Page | 111
IPUE= CPUE (kg/hr-man)x buying price (Php/kg)
V. RESULTS AND DISCUSSIONS
There were six local names they used to know about
bivalves (Table 1) such as
โ€œbalisahaโ€,โ€œamahongโ€,โ€tagnipisโ€,โ€punawโ€,โ€sinaoโ€,โ€silhiโ€,โ€
imbaoโ€ , โ€œwasayโ€ and most common local termwas โ€œlitobโ€.
Each local term denoted different species such as for
balisaha (A.squamosa), amahong (M.philippinarum),
punaw (Kataleysia recens and K.hiantina) , imbao
(A.corrugata), wasay( Pinna bicolor, P.muricata, Atrina
vexillum and A.lamellata). It was also noted that for some
species of bivalves there were different local terms in each
town just like in the case of T.belcheri, Circe scripta,
T.virgata,T.linguafelis and T. staurella which in Clarin they
were named as tagnipis, for Tubigon was sinao while in
Calape it was sihi. However, for species not mentioned they
termed it as litob.
The collection of these bivalves was done in the morning
from 5am to 11 am by handpicking. Usually done, during
low tide when water was clear and siphon of bivalve were
easily seen for faster collection. Among the three towns it
was in Calape and Clarin where high volume of catch was
observed. Although, the collection time is higher in Tubigon
it appeared to have the lowest catch. This low value of .6
kg/hr-man Catch Per Unit Effort (CPUE) observed in
Tubigon showed that there were decreasing number of wild
stocks. This low CPUE value according to Luchavez and
Abrenica (1997) means that there were relatively low wild
stocks of bivalve in the area. Yet, there were other factors
that affect its abundance which could be by environmental
factors like physic-chemical parameters and habitat loss.
Meanwhile, highest CPUE value was observed in Clarin
with 1.2kg/hr-man which also showed more wild livestock
of bivalves. This was followed by Tubigon with .6kg/hr
CPUE value. The harvested bivalves were used both for
consumption and sold in local markets.Frequent gleaners in
Clarin have the highest Income Per Unit effort (IPUE) of 60
pesos per hour. This was followed by Tubigon (45 Php/hr-
man) and Calape had the lowest IPUE of 40 pesos per hour.
The number of hours of collection was highest in Tubigon
and the price value of bivalves which inferred that
collection of these economically important bivalves was
their means of livelihood and they were dependent on them
compared to that of Clarin and Calape.
Table 1. Information on the Bivalve CPUE in Bohol N= (61).
VI. CONCLUSION
Catch per unit effort value of bivalves in Northwestern
Bohol, Philippines is low considering the number of hours
spent in the collection. This lowyield will cascade on the
low economic status of fishermen in the area. Thus, it is
important that there should be law regulating the collection
of these commercially important bivalves for its
sustainability.
ACKNOWLEDGEMENTS
The writers would like to extend their thanks to DOST-
ASTHRDP for the financial support of the study.
International journal of Rural Development, Environment and Health Research (IJREH) [Vol-3, Issue-3, May-Jun, 2019]
https://dx.doi.org/10.22161/ijreh.3.3.5 ISSN: 2456-8678
www.aipublications.com/ijreh Page | 112
REFERENCES
[1] A. Clabrase,J.R. Maclness,D.A. Nelson,R.A. Greig, P.
Yevich. 1984 Effects of long-term exposure to silver and
copper on growth, bioaccumulation and hispathology in blue
mussel. Mytilus edulis. Marine Environmental
Research.Vol.11-pp 253-274
[2] A.De Guzman, Z. Sumalde, M.D. Colance, M.F.Ponce, G. M.
Rance.2014. Economics of Reef Gleaning in the Philippines:
Impacts on the Coastal Environment,Household Economy
and Nutrition. Gaia Resource and Environmental Consultancy
Services, Purok 6, Poblacion, Naawan, Misamis Oriental,
Philippines pp1-4
[3] J. A. Luchavez and B.T.Abrenica. 1997. Fisheries profile of
Bais Bay, Negros Oriental. Silliman Journal, 37(3/4), 93-171.
[4] M.B.Medeiros. 1997. Caracterizaรงรฃo das comunidades de
macroinvertebrados bentรดnicos da Bacia do Cรณrrego Riacho
Fundo, Brasรญlia/DF, e uso destas como bioindicadores de
qualidade de รกgua. Master Thesis. Departamento de Ecologia
Universidade de Brasรญlia, Brazil, 82 p.
[5] D.Roberts. Malacological Society, Commercial exploitation
of bivalves. International meeting on Biology andEvolution
of the Bivalvia, London. pp 138 (1999).
[6] A.Shanmugam and S.Vairamani. 2005.Mollusc in Mangroves
a Case Study:Center of Advanced Study in Marine Biology,
Annamali University, p371.
[7] N.V.Subba Rao.1993. Freshwater Molluscs of India. In: Roa
K.S. (Ed.). Recent Advances in Freshwater Biology. New
Delhi. Anmol Publication. Volume 2. pp. 187-202.
[8] A.Tengberg, and A.S. Cabanban. 2013. Lessons learned from
investing in marine and coastal management initiatives in the
East Asian Seas. Marine Policy, 38, 355-364.
Appendix A
SURVEY QUESTIONNAIRE
Name:______________________
Date:_____________
Age:____________
1. How many times do you gleaned in a week?
A)1 B)2 C) 3 D) everyday
2. What time of the day do you prefer to glean?
A) 5am-6am B)7am-8am C)3pm-5pm
3. How many kilos of bivalves to you get every time in an hour of gleaning?____________ ________________________
4. How much do you earn per kilo? ________________________________________
5. How many kinds of bivalves were you able to collect?___________________________________________
6. What are the local names of bivalves captured?_______________________________________
7. How many are you when you do gleaning activity?_______________________________________
8. What gleaning gear do you use?______________________________________________
Thank You!
The researchers

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  • 1. International journal of Rural Development, Environment and Health Research (IJREH) [Vol-3, Issue-3, May-Jun, 2019] https://dx.doi.org/10.22161/ijreh.3.3.5 ISSN: 2456-8678 www.aipublications.com/ijreh Page | 110 Catch Per Unit Effort (CPUE) of Bivalves in Northwestern Bohol, Philippines Margie P. Vito, MSc, Anthony S. Ilano,Ph.D. Department of Biology, University of San Carlos, Talamban Campus, Cebu City Abstractโ€” Catch Per Unit Effort (CPUE) is a measure of status of marine resource in a given area. In this study, bivalve fishery information was gathered using the self-structured questionnaire. There were 61 respondents who were the registered fishermen of Calape, Tubigon and Clarin. Among the three towns it was Clarin where highest mean CPUE was observed with 1.2kg/hr/man. This was followed by Calape with 0.8kg/hr/man and lowest mean CPUE was recorded in Tubigon with 0.6kg/hr/man. High CPUE value means that there are still enough bivalve resources in the area and lowest CPUE means that these resources are endangered.Considering that,the result of this study showed that there is a need to regulate the collection of bivalves with lower wild stocks to avoid loss of these natural resources. Keywordsโ€” Collection, Gleaning Mangroves, Seagrass and Wild stocks. I. INTRODUCTION Bivalves community as part of benthic organisms is considered as an efficient tool of marine fishery assessment. They belonged to mollusks phyla which was considered as the most abundant marine organisms (Subba Rao, 1993). Bivalve species can be found all around the globe in variety of environments, from the poles to the tropics. Over such array, environmental conditions vary such as water temperature, dissolved oxygen, salinity and potential hydrogen. These differences influenced growth, reproduction and survival but on the other hand, it limits their distribution. They are ecologically important since they served as a bio indicator for water pollution. Although, they mostly thrive in clean waters but some species would occur in polluted waters (Medeiros, 1997). They are suspension feeders and these feeding strategies pose different problems with respect to threshold levels of environmental stress (Calebrase et al., 1984). Economically, they areharvested for food and livelihood resource. As a matter of fact, out of total harvested aquatic resources, about 10% of annual food was consumed through bivalve harvesting (Roberts, 1999). They are also very important in shell industry. In the Philippines, majority of the population live in coastal areas with livelihood mostly involving fishing. Majority of coastalhouseholds (53%) are engaged in subsistence fishing particularly gleaning for invertebrates and small fishes. Gleaning is almost a daily activity done during low tide 2-3 hours and is largely confined to sea grass beds, rocky reef flats and occasionally along the edge of mangrove forests. It involves men, women and children with various ages. Most of the gleaners were engaged in this activity for 20-40 years while few have been gleaning for 50 years. Engagement is especially higher (60%โ€“72%) in remote fishing villages and small islands with little access to other income sources (De Guzman et al., 2014). In this regard bivalves which are one of the highly gleaned marine invertebrateswere under shade of endangered species (Shainmugam and Vairamani, 2005). Hence, this study is necessary to know the volume of bivalves caught per gleaning operation in Northwestern, Bohol to know the sustainability of these marine resource. The bivalves were collected in three towns specifically, Clarin, Tubigon and Calape comprising the Northwestern part of the province. These towns constitute 90% of bivalve fishing industry in Bohol because these are coastal municipalities. This study is vital to know the present condition of bivalves in the area. II. OBJECTIVES OF THE STUDY This study generally aimed to determine the catch per unit effort of bivalves in the area. Specifically, it would compare the catch per unit effort of bivalve species caught in each town namely: Clarin, Tubigon and Calape. Species of bivalves will also be noted as well as the income per unit effort. III. MATERIALS AND METHODS The information on bivalve catch in Northwestern Bohol Philippines was done by interview using the self-structured survey questionnaire in (Appendix A). The respondents of the study were the registered fishermen/gleaners in three towns. A total of 61 individuals were the respondents of the study. There were 21 respondents in Clarin, 20 in Tubigon and 20 in Calape respectively. Aside from face-to face interview, an actual field survey was also conducted. Randomly selected fishermen were selected to glean in the sampling area and they were timed fromthe start and end of gleaning activity. IV. DATA ANALYSIS The Catch Per Unit Effort (CPUE) was determined using the daily total catch data as total weight in kilograms and daily fishing time spend for each collector. CPUE was computed using the formula of Bantoto and Ilano (2012): CPUE= Total weight of catch (kg) Totalfishingtime/hr/collector(man) Income Per Unit Effort (IPUE) was calculated using the formula:
  • 2. International journal of Rural Development, Environment and Health Research (IJREH) [Vol-3, Issue-3, May-Jun, 2019] https://dx.doi.org/10.22161/ijreh.3.3.5 ISSN: 2456-8678 www.aipublications.com/ijreh Page | 111 IPUE= CPUE (kg/hr-man)x buying price (Php/kg) V. RESULTS AND DISCUSSIONS There were six local names they used to know about bivalves (Table 1) such as โ€œbalisahaโ€,โ€œamahongโ€,โ€tagnipisโ€,โ€punawโ€,โ€sinaoโ€,โ€silhiโ€,โ€ imbaoโ€ , โ€œwasayโ€ and most common local termwas โ€œlitobโ€. Each local term denoted different species such as for balisaha (A.squamosa), amahong (M.philippinarum), punaw (Kataleysia recens and K.hiantina) , imbao (A.corrugata), wasay( Pinna bicolor, P.muricata, Atrina vexillum and A.lamellata). It was also noted that for some species of bivalves there were different local terms in each town just like in the case of T.belcheri, Circe scripta, T.virgata,T.linguafelis and T. staurella which in Clarin they were named as tagnipis, for Tubigon was sinao while in Calape it was sihi. However, for species not mentioned they termed it as litob. The collection of these bivalves was done in the morning from 5am to 11 am by handpicking. Usually done, during low tide when water was clear and siphon of bivalve were easily seen for faster collection. Among the three towns it was in Calape and Clarin where high volume of catch was observed. Although, the collection time is higher in Tubigon it appeared to have the lowest catch. This low value of .6 kg/hr-man Catch Per Unit Effort (CPUE) observed in Tubigon showed that there were decreasing number of wild stocks. This low CPUE value according to Luchavez and Abrenica (1997) means that there were relatively low wild stocks of bivalve in the area. Yet, there were other factors that affect its abundance which could be by environmental factors like physic-chemical parameters and habitat loss. Meanwhile, highest CPUE value was observed in Clarin with 1.2kg/hr-man which also showed more wild livestock of bivalves. This was followed by Tubigon with .6kg/hr CPUE value. The harvested bivalves were used both for consumption and sold in local markets.Frequent gleaners in Clarin have the highest Income Per Unit effort (IPUE) of 60 pesos per hour. This was followed by Tubigon (45 Php/hr- man) and Calape had the lowest IPUE of 40 pesos per hour. The number of hours of collection was highest in Tubigon and the price value of bivalves which inferred that collection of these economically important bivalves was their means of livelihood and they were dependent on them compared to that of Clarin and Calape. Table 1. Information on the Bivalve CPUE in Bohol N= (61). VI. CONCLUSION Catch per unit effort value of bivalves in Northwestern Bohol, Philippines is low considering the number of hours spent in the collection. This lowyield will cascade on the low economic status of fishermen in the area. Thus, it is important that there should be law regulating the collection of these commercially important bivalves for its sustainability. ACKNOWLEDGEMENTS The writers would like to extend their thanks to DOST- ASTHRDP for the financial support of the study.
  • 3. International journal of Rural Development, Environment and Health Research (IJREH) [Vol-3, Issue-3, May-Jun, 2019] https://dx.doi.org/10.22161/ijreh.3.3.5 ISSN: 2456-8678 www.aipublications.com/ijreh Page | 112 REFERENCES [1] A. Clabrase,J.R. Maclness,D.A. Nelson,R.A. Greig, P. Yevich. 1984 Effects of long-term exposure to silver and copper on growth, bioaccumulation and hispathology in blue mussel. Mytilus edulis. Marine Environmental Research.Vol.11-pp 253-274 [2] A.De Guzman, Z. Sumalde, M.D. Colance, M.F.Ponce, G. M. Rance.2014. Economics of Reef Gleaning in the Philippines: Impacts on the Coastal Environment,Household Economy and Nutrition. Gaia Resource and Environmental Consultancy Services, Purok 6, Poblacion, Naawan, Misamis Oriental, Philippines pp1-4 [3] J. A. Luchavez and B.T.Abrenica. 1997. Fisheries profile of Bais Bay, Negros Oriental. Silliman Journal, 37(3/4), 93-171. [4] M.B.Medeiros. 1997. Caracterizaรงรฃo das comunidades de macroinvertebrados bentรดnicos da Bacia do Cรณrrego Riacho Fundo, Brasรญlia/DF, e uso destas como bioindicadores de qualidade de รกgua. Master Thesis. Departamento de Ecologia Universidade de Brasรญlia, Brazil, 82 p. [5] D.Roberts. Malacological Society, Commercial exploitation of bivalves. International meeting on Biology andEvolution of the Bivalvia, London. pp 138 (1999). [6] A.Shanmugam and S.Vairamani. 2005.Mollusc in Mangroves a Case Study:Center of Advanced Study in Marine Biology, Annamali University, p371. [7] N.V.Subba Rao.1993. Freshwater Molluscs of India. In: Roa K.S. (Ed.). Recent Advances in Freshwater Biology. New Delhi. Anmol Publication. Volume 2. pp. 187-202. [8] A.Tengberg, and A.S. Cabanban. 2013. Lessons learned from investing in marine and coastal management initiatives in the East Asian Seas. Marine Policy, 38, 355-364. Appendix A SURVEY QUESTIONNAIRE Name:______________________ Date:_____________ Age:____________ 1. How many times do you gleaned in a week? A)1 B)2 C) 3 D) everyday 2. What time of the day do you prefer to glean? A) 5am-6am B)7am-8am C)3pm-5pm 3. How many kilos of bivalves to you get every time in an hour of gleaning?____________ ________________________ 4. How much do you earn per kilo? ________________________________________ 5. How many kinds of bivalves were you able to collect?___________________________________________ 6. What are the local names of bivalves captured?_______________________________________ 7. How many are you when you do gleaning activity?_______________________________________ 8. What gleaning gear do you use?______________________________________________ Thank You! The researchers