Revised]
-
Upload
mary-beth-pillazo-aranas -
Category
Documents
-
view
161 -
download
20
Transcript of Revised]
MISAMIS OCCIDENTAL NATIONAL HIGH SCHOOL
S.Y. 2011-2012
Relative Abundance of Starfish in
Lower Loboc, Oroquieta City
Researchers:
Arañas, Mary Beth P.
Dapin, Yemie G.
Dugso, Dariel Jade B.
Pagtalunan, Kyla Veronica D.
Rivayle, Doly E.
Acknowledgement
The researchers were helped in the development of this study by the encouragements,
criticism, editing, recommendations and the accommodations of many people.
Heartfelt thanks to Mrs. Solly Namocatcat, the research adviser, for her assistance,
professional guidance, appropriate comments and suggestions, raising precautions and
eventually for educating us towards the success of this project since the very start and this
study.
We are thankful to Mr. Gabriel A. Daison and his group mates in Research for putting
so much time, effort and spirit in helping this project, answering our billion questions and for
being there accepting our queries.
We are forever indebted to our parents for the guidance, understanding, love, moral
and financial support which made the researchers inspired of their everyday lives.
We are thankful to our brothers and sisters for their concerns and moral support and
who shared their time and also who lent their resources for the making of this study.
We were very thankful to our classmates, who also gave some comments,
suggestions, ideas which had been very useful.
Most of all, To God, the author of life, glory and honour be unto Him. For His gift of
knowledge and wisdom, guidance and protection, the researchers were able to sustain the
everyday needs and made the study possible.
i
ABSTRACT
Quantitative data shows that salinity and pH of the sea water provides the difference
on the number of seastars found in one area. Also, with both site samples having nearly
identical averages on the temperature further supports that.
The results of the study further support previous study on the abundance of starfish
conducted by R.G.Crump et.al (1983) on the natural history, life history and ecology of the
two British species of Asterina. This supports the study that seastars can live in sea water
with specific amount of pH which is 8 and salinity with a range of 28-35ppt or specifically on
normal sea water which has a pH of 8 and salinity of 35ppt but in temperature, starfish can
live in either high or low temperature because of its special features.
This leads to the conclusion that physico-chemical parameter affects the number of
starfish present in seawater: the pH of seawater affects the number of starfish, the salinity of
seawater affects the number of starfish and the temperature of seawater affects the number of
starfish.
Based on the results of the study conducted, the researchers concluded the following:
In Site 1, the present species of starfish are Horned Sea Star(Protoreaster nodosus), Serpent
star(Ophiarachna incrassate), Black Brittle Star(Ophiomastix variabilis), Spiny Cushion
Starfish(Culcita schmideliana), Blue Star(Linckia laevigata). While in Site 2, the present
species of starfish are only Horned Sea Star (Protoreaster nodosus) and Black Brittle Star
(Ophiomastix variabilis). The temperature of the water in Site 1 is 29.5 o C while in Site 2 is
30 o C. The salinity in Site 1 is 34.33ppt while in Site 2 is 33.83ppt. The pH level in Site 1 is
7.83 while in Site 2 is 7.2.
ii
TABLE OF CONTENTS
Acknowledgement. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . i
Abstract. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . ii
Introduction. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 1
Methodology. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 5
Results and Discussion. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 7
Conclusions and Recommendation. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 10
Definition of Terms. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 11
Bibliography and Webliography. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 12
INTRODUCTION
Background of the Study
Seawater quality varies gradually because it is open to other seas and oceans. Debris
coming water vehicles and land are carried from shore to shore. Nowadays, massive part of
the earth’s water is polluted due to human’s improper waste disposal. Living things are
dependent to their environment like humans and plants to land, birds to the air and wind and
aquatic creatures to water.
Lots of sea organisms are already used as bioindicators of water pollution. A previous
study used starfish as a bioindicator of metal pollution. Metals like Cd, Pb, Zn and Cu in
starfish Asterias Rubens (Storelli MM, et al.2005). The result indicates that metal pollution
can affect the color and structure of a starfish.
In this study, researchers are going to determine if the physico-chemical parameter
affects the number of starfish to indicate water pollution. Researchers will compare the
number of starfish in the two stations in the coast of Lower Loboc. This research can help in
the community by making them how whether the physico-chemical parameter affects the
number of starfish or not so that they can reflect and be aware of their reactions in the future
and to motivate them to help our environment.
Objectives of the Study
The study aims to determine the diversity of starfish. The study specifically it aims to:
1. Identify the present species of starfish in both sites.
2. Measure the physico-chemical parameters such as temperature, salinity and pH in
both sites.
3. Determine the relative abundance of each of species of starfish found in both sites.
Scope and Limitation
The study is limited only to the abundance of starfish in the Intertidal Zone in El
Triunfo and Uncle Greg’s beach. This study is only concern to the starfish inside the
intertidal zone in El Triunfo and Uncle Greg’s beach excluding the starfish that are found in
other beaches.
Significance of the Study
The result of the research will inform the people by the current status of the starfish
and the water in the intertidal zone of Lower Loboc, Oroquieta City. With the help of this
research, the people will know if there is a need for them to take action and what action will
the people take because it may alter other marine creatures.
Review of Related Literature
A starfish is a marine invertebrate. Invertebrates make up around about 95% of the
animals in the ocean, so they are the most common major group. Starfish belong to a phylum
or a big group of animals called echinoderms and that include starfish, sea urchins, brittle
stars, sea cucumbers and something called feather star. Starfish are predators, and they’re
probably the most important predator in the shallow ecosystem so the depths where we could
dive or swim. They eat basically anything that they can come across. Their feeding activities
control the whole ecosystem. It comes back to the concept of keystone species. If that species
is affected, it is going to have a disproportionately greater effect on the whole ecosystem
(Lamare, 2009).
The water activity and pH ranges for growth of Glaciecola punicea (a psychrophile)
were extended when this organism was grown at suboptimal rather than optimal
temperatures. No such extension was observed for Gelidibacter sp. Strain IC158 (a
psychrotolerant bacterium) at analogous temperatures. Salinity and pH may be primary
physico-chemical parameters controlling bacterial community development in sea ice (D.S
Nichols et al., 1999).
A genericindex(GI)- the ration of abundance of Achnanthes, occonies and Cymbella,
to that of Cyclofella, Meiosira and Nitzchia- was used to measure changes the diatom
assemblages. GI values correlated well the saprobic index, diatom assembles index,
composite river water quality index and species richness of insects (Jiunn-Tzong Wu, 1999).
The results also showed that the two most important parameters studied that were inversely
related to the invertebrate scores (P.S Hooda, et al., 2006). Previous field and laboratory
studies have identified the alga Labophora variegate as a good candidate for biomonitoring
metal contamination in the New Caledonia lagoon which is subjected to intensive and
extensive metal inputs from land-based mining activities (Laetitia Hedouin et al 2008).
The comparison of mean oocyte diameters, gonodal indices and gonado-somatic
relationships of specimens captured in polluted areas with individuals from unpolluted
reference sites revealed a significant decrease of these parameters with increasing water
pollution. High loads of organic and industrial savage are considered responsible for the
effects of an increasing downriver pollution gradient on the reproductive system of Astyanax
fasciatus. Condition factors showed an inverse relationship, increased significantly in
downriver polluted areas. The declining gonodal indices showed that energy was allocated to
somatic growth. The results of the study recommend the use of A-fasciatus in biomonitoring
essays (Schulz et al 2001).
The inhibitive effects of salinity, in this case, were investigated. The aromatic
compounds were obtained from an oil-servicing firm in Port Harcourt, and the microbial
analysis was conducted on the water samples for the purpose of identification, isolation and
characterization of the Pseudomonos putida. A head-to-head comparison of the degradation
obtained from experiments conducted. The result showed that salinity did not inhibit the rates
of toluene, phenol and benzene in fresh medium was done based on the data degradation rate
of toluene and benzene. However, phenol was significantly affected by salinity. The aromatic
compounds removal from water solution varied depending on the conditions, that is, the type
of compound, the composition of the water solution and the conditions of their exposure. The
results obtained from this investigation was compared with Suietlik et al, (2009) work which
revealed 22 to 28% reduction in aromatic compounds degradation while the present research
shows 45-75% reduction in aromatic compounds under investigation for a period of 2 weeks
(21 days) exposure. The parameters form the bedrock for further improvement of the kinetic
models and also, serve as an outline for possible pilot-scale bioremediation by engineers (C.P
Upaka 2010).
Attempts were made to study and analyze the physico-chemical characteristics of the
water. Various parameters like Temperature, pH, Total suspended solids, and Total dissolved
solids, Alkalinity, Dissolved oxygen, Chemical Oxygen Demand, Nitrate, Chloride, Sodium,
Potassium, Phosphate, Fluoride, Total Coli Forms (Pond water) etc. give a picture of quality
parameter in both dug well and bore well water as well as pond water of the town (M.R
Mahananda et al 2010).
METHODOLOGY
Study Area
The Intertidal Zones of El Triunfo and Uncle Greg of Oroquieta City contains many
marine species particularly the starfish. For the study of ecology, the Intertidal Zones of El
Triunfo and Uncle Greg of Oroquieta City is an important model system.
Physico-chemical Parameter
1. Temperature
Laboratory thermometer was used to measure the temperature of the water of site
which was clipped 10 cm below the water. The reading of temperature was recorded after 3
minutes.
2. Salinity
The researcher collected sea water in each quadrat and was brought to the Agriculture
Department in Oroquieta City to be able to determine the salinity using refractometer.
3. pH testing
Researcher describes a substance’s level of acidity using the pH meter. The
researchers collected sea water and dipped it on a pH paper to determine the acidity of the
water.
Biological Sampling
Two stations were sampled in each of the Intertidal zones of El Triunfo and Uncle
Greg using transect quadrat method having 2m x 2m made up of straw. The straw was tied to
a stick connected from one stick to another to form a square and shoved on the
water.
The starfish in each quadrat of two intertidal zones were counted and sample of each species
were taken using bare hands. The collected starfish is placed in a container with enough sea
water and were labeled with its quadrat number.
Identification
Starfish are distinguished according to their taxonomic identification. Researchers
identified them using the sample photos provided by Teresa Zubi (2010).
Experimental Flow
Selection of Sampling Sites
Determination of Physico-Chemical Parameters
Collection of Samples
Identification of Samples
RESULTS AND DISCUSSION
Researchers measured the temperature, the pH of the water and the salinity of the two
sampling sites.
Table 1. Physico-chemical Parameters of the Two Sampling Site
Site1(Uncle Greg’s Intertidal Zone)
Site2(El Triunfo’s Intertidal Zone)
Q1 Q2 Ave Q1 Q2 Ave
Temperature 29 30 29.5 30 30 30
pH 7.9 7.7 7.8 7.2 7.2 7.2
Salinity 34.7 33.9 34.3 34.2 34 34.1
The data gathered as shown on the table above, revealed:
The average water temperature in Site 1 is 29.5o C while in Site 2 is 30o C. The water
temperatures on both sites are between the normal value range as based on the Marine
Science article from the Marine Bio website (Considering the country’s tropical location).
Average water pH level in Site 1 is 7.83 while Site 2 is 7.2 which are below the
normal pH of seawater which is 7.5-8.5 according to a Marine Science article from the
Marine Bio website. Having higher pH means more concentration of alkaline while lower pH
means acidic which both higher or lower pH value can kill marine life which includes
starfish, thus indicating that the pH value of station 1 is still at its normal value while station
is slightly lower than normal pH level (http://www.marinebio.net/).
Average water salinity of Uncle Greg is 34.33 while in El Triunfo is 33.83 which is
only station 1 was able to reach the normal salinity range, which is 34-35ppt according to
Marine Science article from the Marine Bio website.
Graph 1. The Comparison Between The Average of the Physico-Chemical Parameters in
The Two Sampling Sites
From the data as shown on the graph above, the following have been noted:
The average temperature in Site 1 is lower than in Site 2. The average pH of the water
in Site 1 is higher than in Site 2. In other terms, the water in Site 1 is more acidic than in Site
2. The average salinity in the water in Site 1 is slightly higher than in Site 2.
Table 2. The Number of Starfish Present In The Intertidal Zone of Site 1(Uncle Greg’s Beach
Resort) and Site 2(El Triunfo Beach Resort) in Lower Loboc, Oroquieta City
Starfish 1Horned Sea
Star – (Protoreaster nodosus)
Starfish 2Serpent
star (Ophiarach
na incrassata)
Starfish 3Black brittle
star (Ophiomast
ix variabilis)
Starfish 4Spiny
Cushion Starfish (Culcita
schmideliana)
Starfish 5Blue Star (Linckia
laevigata)Total
Site1 10 5 6 1 1 23
Site 2 3 0 1 0 0 4
Total 13 5 7 1 1 27
To determine the relationship between starfish and its corresponding physico-
chemical parameter, the mean on the three-day data gathering was compared to the data
collected on the period.
The data shown on the table above indicate that salinity and pH of the sea water
provides the difference on the number of starfish found in one area. Also, with both site
samples having nearly identical averages on the temperature further supports that.
The results of the study further support previous study on the abundance of starfish
conducted by R.G.Crump et.al (1983) on the natural history, life history and ecology of the
two British species of Asterina. This supports the study that starfish can live in sea water with
specific amount of pH which is 8 and salinity with a range of 28-35ppt or specifically on
normal sea water which has a pH of 8 and salinity of 35 ppt but in temperature, starfish can
live in either high or low temperature because of its special features.
Table 3. The Relative Abundance of Each Species of Starfish Found In the Intertidal Zone
of Lower Loboc, Oroquieta City
Starfish 1Horned Sea
Star – (Protoreaster nodosus)
Starfish 2Serpent
star (Ophiarach
na incrassata)
Starfish 3Black brittle
star (Ophiomast
ix variabilis)
Starfish 4Spiny
Cushion Starfish (Culcita
schmideliana)
Starfish 5Blue Star (Linckia
laevigata)
RelativeAbundanc
e48.15% 18.52% 25.93% 3.70% 3.70%
The table above shows the following:
The relative abundance of Starfish 1(Protoreaster nodosus) is the greatest among all
the species present in the the two sites in the intertidal zone of Lower Loboc, Oroquieta City
having a relative abundance of 48.15%. Second greatest is Starfish 3(Ophiomastix variabilis)
having a relative abundance of 25.93%. Third greatest is Starfish 2(Ophiarancha incrassate)
having a relative abundance of 18.52%. While the least among the five species found in the
two sites in the intertidal zone of Lower Loboc, Oroquieta City are Starfish 4(Culcita
schmideliana) and Starfish 5(Linckia laevigata) for both having relative abundance of 3.70%.
CONCLUSION
Based on the results of the study conducted, the researchers concluded the following:
1. In Site 1, the present species of starfish are Horned Sea Star(Protoreaster nodosus),
Serpent star(Ophiarachna incrassate), Black Brittle Star(Ophiomastix variabilis),
Spiny Cushion Starfish(Culcita schmideliana), Blue Star(Linckia laevigata). While in
Site 2, the present species of starfish are only Horned Sea Star (Protoreaster nodosus)
and Black Brittle Star (Ophiomastix variabilis).
2. The temperature of the water in Site 1 is 29.5 o C while in Site 2 is 30 o C. The salinity
in Site 1 is 34.33ppt while in Site 2 is 33.83ppt. The pH level in Site 1 is 7.83 while in
Site 2 is 7.2.
3. The relative abundance of Starfish 1(Protoreaster nodosus) is 48.15%, Starfish 3
(Ophiomastix variabilis) is 25.93%, Starfish 2 (Ophiarancha incrassate) is 18.52%,
both Starfish 4 (Culcita schmideliana) and Starfish 5 (Linckia laevigata) are 3.70%.
RECOMMENDATION
The number of starfish in normal conditions of physico-chemical parameters is a good
sign that the site with normal conditions is good habitat for the starfish. This study has only
investigated the effect of physico-chemical parameter to the number of the starfish. Based
upon the findings of the study, the researchers would like to recommend the following:
1. Further research is required to find out if there is other marine life that is
affected to the signs given by the data.
2. Use other physicochemical parameters to identify the effect of it to the
relative abundance of starfish.
3. Continue the monitoring of physicochemical parameters in the Intertidal
Zone of Lower Loboc, Oroquieta City.
DEFINITION OF TERMS
Starfish- any marine invertebrate of the class Asteroidea (phylum Echinodermata) having
rays, or arms, surrounding an indistinct central disk. Despite their older common name, they
are not fishes (http://www.britannica.com). In this study, it refers to the organism collected at
Lower Loboc shoreline.
Physicochemical Parameter- refer to the physical and chemical characteristics and
definition of an object. In this study, physical parameters refer to the water temperature,
salinity and pH.
BIBLIOGRAPHY
Ansa-Asare, O.D. and Karikari, A.Y. 2003. Physico-chemical and Microbial Water Quality Assessment of Densu River of Ghana. CSIR-Water Research Institute, Accra, Ghana
Behera, N.R. et al. 2010. Physico-chemical analysis of surface and ground water of Bargarh District, Orissa, India. Department of Environmental Sciences, Sambalpur University, Orissa, India
Bustamante, P. et al. 2008. The Tropical Brown Alga Lobophora Vanegata as a Bioindicator of Mining Contamination in New Caledonia Lagoon. Elsevier Ltd Publishing, New Cadelonia, France
Chambost-Manciet, Y. et al. 2003. Echinoderms as bioindicators, bioassays, and impact assessment tools of sediment-associated metals and PCBs in the North Sea. Laboratoire de Biologie Marine, Université Libre de Bruxelles
Greenhill, A.R. et al. 1999.Physicochemical Parameters for Growth of the Sea Ice Bacteria Glaciecola punicea. Application Environment Microbiol Vol. 65 no. 8: 3757-3760
Storelli, MM. 2005. Bioindicator Organism: heavy metal pollution evaluation in the Ionian Sea (Mediterranean Sea). Italy: Springer
Ukpaka, C.P. 2010. Biodegradational model on effect of some physicochemical parameters on aromatic compounds in fresh water medium. Journal of Bacteriology Research Vol. 3(3), pp. 42-55
Wu J.T. 1999. A Generic Index of Diatom Assemblages as Bioindicator of Pollution in the Keelung River of Taiwan. Netherlands: Kluwer Academic Publishers.
WEBLIOGRAPHY
Anderson, G. 2003. Seawater: Composition. Retrieved October 8, 2008 from http://www.marinebio.net/
Bellingham, K. 1999. Physicochemical Parameters of Natural Waters. From http://www.stevenswater.com
Caprette, D. 1995. Writing Research Papers. Retrived November 10, 2011 from http://www.ruf.rice.edu
Coteur, G. et al. 2009. Long-term environmental exposure to metals (Cu, Cd, Pb, Zn) activates the immune cell stress response in the common European sea star (Asterias rubens). Retrieved September 28, 2011 from http://www.ncbi.nlm.nih.gov
Hooda, P.S. et al. 2006. Macroinvertebrates as Bioindicators of Water Pollution in Streams Draining Dairy Farming Catchments. Retrieved June 26, 2000 from http://www.tandfonline.com
Martins-Junior, H. and Schulz, U. H. 2000. Astyanax fasciatus As Bioindicator of Water Pollution of Rio dos Sinos, RS, Brazil. Retrieved November 30, 2001 from http://www.scielo.br
Thompson, Z. 2010. Guidelines for writing methodology for dissertation proposal. Retrieved September 6, 2010 from http://helpwithassignment.blogspot.com