chemistry ip draft 3 22
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Chapter I
INTRODUCTION
Background of the Study
Manila Bay is one of the best natural harbors of the world because of its appropriate geography
and in turn, it has become one of the premier international gateways to the countrys political, economic,
and social centers. With this strategic importance, many manufacturing industries are now found here
and the bay is now home to tanneries and jewelry making, electronics, and plastic industries among
others. These changes in human activity have change the natural environment of the area is now facing
various threats: over population, pollution discharges, and ecosystem deterioration. One particular threat
is the extinction of important marine life, which live in the area due to overexposure to the contaminants
caused by human activity.
Certain conditions in our waterforms make them suitable for sustaining marine life. If these
standards arent met, less and less marine life will survive our waters up to the point that the area
becomes biologically dead: when oxygen levels are so low that it cant support life anymore. Less
marine life will result to more consequences both environmentally and economically. If the water is
severely polluted, it needs to be restored so that it can sustain marine life.
The alarmingly increasing damages wrought on to its ecosystem results in socio-economic losses
estimated at an average of Php 4 billion yearly: 48% of which (Php 1.92 billion) accounts for fishermen
due to red tide. These economic losses will eventually be worse if no action is taken to prevent them;
they also reflect the urgency of the situation with regards to our environment.
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The fact that the Philippines is one of the megadiverse countries in the world due to its
tremendous amount of resources means that some of them might not be consumed properly. One such
example are crab shells which, after the meat of crabs are eaten, are only used as decorations or
ornaments. In addition to this, potassium alum or tawas is also very popular, but only for use as a
deodorant. There are studies that have shown that components in crab shells and potassium alum may be
used to help in reducing pollutants in our waters.
This inspired our group to go beyond that aesthetic aspect of crabs and made a treatment where
crabs and potassium alum can be used to remove contaminants from the seawater at Manila Bay. The
study compares three areas of the bay and how much lead will be reduced once they undergo the
treatment. This study can help the Department of Environment and Natural Resources, the Department
of Science and Technology, and the Department of Health in creating innovative ways to help in
cleaning our waters and promoting a healthy environment for everyones benefit.
This study was aimed to:
General Objectives
Determine if chitin and/or aluminum sulfate can be used to lessen the lead content of water inManila Bay.
Specific Objectives
Observe and determine the physical characteristics of water samples from Manila Bay usingpH, and temperature tests.
Improvise a filtering process that includes the use of chitin and potassium alum for thetreatment process.
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Measure and analyze the lead content of the said samples both before and after thetreatments.
Significance of the Study:
Metals are found in the environment all around the world, mostly because of human activities.
Industrial activities have led to very high heavy metal concentrations on the environment, which are in
general significantly higher than those in the Earths crust, which presents the lurking dangers of
exposure of organisms to such contaminants, not only decreasing marine biodiversity, but exposing
human beings and cause harmful effects on them.
Lead, in particular, us a very poisonous metal regardless of intake and affects every organ in the
body. It mainly affects the nervous system, and long-term exposures can lead to weakness in joints, and
severe damage to the brain and kidneys. It also causes harmful effects to marine life, which may lead to
eventual extinction, and serious losses in resources may occur if such an event may happen.
Manila Bay is a natural harbor which serves the Port of Manila. It facilitated commerce and trade
between the Philippines and its neighboring countries and became a gateway for commerce and trade
between the Philippines and its neighboring countries. According to theManila Bay Coastal Strategyby
PEMSEA, Manila Bay provides many uses for the community: employment, income, services. More
than 50% of the countrys products come from it: fishing and aquaculture, manufacturing, shipping,
agriculture, mining, quarrying, and tourism.
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Additionally, the UNDP Regional Programme on Building Partnerships in Environmental
Management for the Seas of East Asia (PEMSEA) stated that the Manila Bay has an annual economic
value of Php 8 billion at its lowest. Today, it faces a serious environmental threat: pollution. With
industrialization, overexploitation of its resources is now causing pollution and destruction of habitats,
increase of pollution, and the death of marine life because of the uncontrolled contamination of the bay.
The destruction of marine life in an ecosystem can cause many catastrophic damages
environmentally, economically, and aesthetically. Using the concept of the food chain, with the
extinction of one species, there will be a chain reaction, and many other organisms will be depleted of
food and eventually, we too will be affected with this decline.
With this study, new methods of treating lead-contaminated water can be explored, particularly
with the use of materials which are usually disposed of after consumption (e.g. crab shells). The study
can help avoid wastage of materials by recycling, and help save resources which communities,
especially the poor living near the bay, may make use of in order help save the environment without the
need to spend too much, and in the future, restore the economic balance in our country because our
natural resources will have been restored and benefitting our country by promoting the conservation of
our environment.
Scope and Delimitation:
The researchers collected samples from three areas of Manila Bay: the coastline at Roxas
Boulevard in Manila City, one from a point deeper than the coastline, and a point near the center of the
bay to be used as subjects for the testing. The the location of the collection was at Roxas Boulevard
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across Aristocrat and Maxs Restaurants on January 26,2013 at 1:13 pm, 1:01 pm, and 1:07 pm for the
coast, off-shore, and deep shore locations, with respective distances of 0 m, 60 m, and 110 m off-coast.
A filter process using chitin was used to pour the water through to remove contaminants or
impurities from the water. Potassium aluminium sulfate (tawas) will be acquired from the supermarket
for use in this study. The budget used for this study was estimated to be around Php 700 800. To
determine its lead content, samples were sent to the laboratory for analyzing to determine the amount of
lead content present before and after the treatment process. The water samples will be subjected to 2
tests to determine their physical characteristics: pH test, and temperature test before and after being
subjected to the purification process. The study will use the same 3 samples for the tests to determine
their water quality. Furthermore, the thermometer can take measurements up to one decimal place.
(0.1.To determine the quantity of lead concentration of the samples used in the study, an Atomic
Absorption Spectrophotometer was used in UP Diliman, Quezon City using mg/L (milligrams per liter)
as a unit of measurement. It is commonly used as a unit of concentration for liquids to measure to
amount of a certain chemical or substance per volume of water, which is appropriate for this study
which deals with water quality.
Finally, the researchers focused on the effect of the chitin and potassium alum in terms of the
percentage of decrease in the lead content of the collected water samples. The researchers were not
focused on determining changes, temperature, or the maximum limit of reduction of lead content
percentages for the water samples. Furthermore, the nitrite, nitrate and ammonium, and phosphates were
measured only to attain an overview of the condition of the bay at the time of collection, these
information are not necessarily intended to significantly determine the lead concentration.
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Chapter II
REVIEW OF RELATED LITERATURE
Water is one of the most important resources to most life in our planet, especially for us humans.
Biologically speaking, water makes up approximately 70% of adult humans. Almost all industries use
water in one way or another, and to top it all of, it practically makes three fourths of our planet.
However, with the advent of the Industrial Revolution, problems with water pollution have
arisen and have worsened today. Water pollution is defined as a body of water that is "adversely affected
due to the addition of large amounts of materials" (Krantz, 1996). This means that when a body of water
is not anymore suitable for its original purpose, it is deemed "polluted". There are multitudes of ways
wherein this can happen. One example is a direct form of pollution, such as an oil spill. According to
studies made by the World Water Assessment Programme in 2003, an estimated 2 million tons of
sewage, industrial, and agricultural waste is thrown into our worlds water. Furthermore, this problem
also affects inland life: globally, 24% of mammals and 12% of birds connected to inland waters have
been considered threatened.
Many factors may point to evidences of water pollutions, some of which are nitrites, nitrates and
ammonium, and phosphates. Nitrates and nitrites are some of the chemicals that are produced during the
nitrogen cycle and are predominantly used for fertilizers and food preservatives, respectively.
Meanwhile, ammonium is a polyatomic ion that is formed when ammonia reacts with a base; and
phosphate is another polyatomic ion which is a salt of phosphoric acid.
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meters, which resulted in an estimated mean pH of 8.34, which is higher in alkalinity in comparison to a
neutral 7 for water in normal conditions.
Instead of expensive treatments, the use of biological materials is a good alternative to reduce
lead in seawater. One such example is chitin: it is the second most common organic compound in nature
and is a polysaccharide, forming the basis of hard shells of crustaceans, such as crabs. Pastor (2004) said
that chitin has applications in pharmaceutical, biomedical, food, agricultural, paper, cosmetic and textile
industries, as well as in chromatography. Additionally, Domard and Muzzarelli (2000) said that
considerable amounts of chitin are used for water treatments. The application of chitin and chitosan in
water treatment focuses mainly in coagulation-flocculation processes to remove organic residues,
suspended solids, amino acids and dyes. Lontoc, Mendoza, Rasco, Salvador, Yap (2003) said could be
obtained as a powder after dissolution of calcium and studies have shown it to have potentials in treating
basic and acidic water treatment. According to a study by Peiselt da Silva, K.M., et al., one of the most
important properties of chitin is removing is its ability to remove metal ions. This is supported by
Muzzarelli, R.A.A., et al., who said that their structure allows excellent complexation capacity with
metal ions, particularly transition and post-transition metals.
Furthermore, chitin has been proven to remove heavy metals by Saravanan, et. al., of
Sathyabama University, India. The essentiality of removal of heavy metals was discussed, along with
adsorption studies have been used to remove Cr (VI) from aqueous solutions using chitin composites. It
was suggested that chitin can be used to remove heavy metals to attain a more favorable quality of
water. A similar study was made by D. Zhou, et al., of the Wuhang University in China with the
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adsorption of metals in aqueous solutions by chitin. It was proven that chitin can effectively adsorb lead
(II), cadmium (II), and copper (II) ions. This was influenced by the properties of metal ions, specifically
electronegativity.
Additionally, potassium alum may also be a possible solution to this problem. According to
Anne Marie Helmenstine, Ph.D. of About.com, is also known as potash alum or tawas, in the Philippines
and is a mineral salt. It is also known as simply alum. It was known to have been used in Roman times
as for water purification. It's chemical formula is KAl(SO4)2. It can be used to bond to impurities in
water and settle them at the bottom, and this type of water purification is known as coagulation.
A past study was made by Johnson, Girinathannair, Ohlinger, Ritchie, Teuber, and Kirby and
published in 2008, which made use of alum, other mineral salts and ferric chloride to test their efficiency
in the removal of heavy metals in wastewater through coagulation. Different analytical methods were
used such as jar tests, total suspended solids analyses, and the use of spiking solutions. The study
showed a 95% removal efficiency in lead, 79% in copper, 57% in zinc, and 17% in nickel. Alum and
ferric chloride increased the removal of total suspended solids as well as the optimum settling,
specifically from 45 minutes to 25 minutes.
With the pollution present at Manila Bay, many risks and challenges are present for the
communities, which thrive through it especially fishermen, which have the water resources as their most
important and vital source of income. According to the Manila Bay Coastal Strategy, the economic and
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social losses brought by deterioration of the Bay waters and consequent decline in economically
important resources are felt most by the fisherfolks, particularly those who depend on subsistence
fishing.
With these problems, the researchers will conduct tests for this study which will involve mainly
the biochemical oxygen demand and the dissolved oxygen of the water. refers to the amount of oxygen
that would be consumed if the organics in one liter of water were oxidized by bacteria and protozoa.
When BOD levels are high, dissolved oxygen (DO) levels decrease because the bacteria are consuming
the oxygen that is available in the water. Since less dissolved oxygen is available in the water, fish and
other aquatic organisms may not survive.
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Chapter III
METHODOLOGY
Materials/Equipment:
Quantity Specifications Description of Material
3 500 mLwater samples from manila
bay
500 mL Wilkins distilled water
5 pcs. locally available crab and shrimp shells
50 gacquired from the
supermarket
potassium aluminium
sulfate (tawas)
500 mL 4% concentration sodium hydroxide solution
500 mL 4% concentration hydrochloric acid solution
20 g Activated charcoal
80 g N/A sand
1 pc. medium-sized basin
4 pcs. 400 mL-capacity beakers
1 pc. 50 mL-capacity beaker
1 pc. porcelain bowl
4 pcs. iron tripods
4 pcs. glass funnels
1 pc. glass stirring rod
3 Glass jars
1 medium basin
12 pcs. N/A universal pH indicators
1 pc. aquarium thermometer1 pc. glass Graduated cylinders
1 pc. Small-sized Water container
May vary*Laboratory-use
(preferably latex)Gloves
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General Procedure / Treatment:
PREPARATION OF MATERIALS
A. Acquisition of water samplesWater samples were collected from the coastlines of Manila bay: fifteen 500 mL samples
from each location: one from the coastline, one from a point deeper than the coastline, and a
point near the center of the bay, for the three tests. Nine of which were used for the physical
tests, 3 of which were used as control samples and were tested before the treatment process, and
three of which were used for the treatment.
B. Creation of Acid and Base SolutionsIn order to attain a 4% concentration of hydrochloric acid, 8.33 mL of a 12 M solution
was added to 1000 mL of distilled water and stirred. Afterwards, 4 g of sodium hydroxide was
added to 1000 mL of distilled water to attain a 4% sodium hydroxide solution. Solutions with pH
of 2 and 12 were recorded for the hydrochloric acid solution and sodium hydroxide solution.
C.Extraction of ChitinCrab and shrimp shells were collected, washed, air-dried, and ground. To remove the
protein residues, 50 g each of the powdered crab shells were treated with 500 mL of the NaOH
solution. It will be stirred as a mixture for 30 minutes, decanted and the solid particles washed
with distilled water. 500 mL of HCl solution will then be added. The mixture was stirred for 30
minutes. The solid particles obtained after filtration was the chitin. It was air-dried and weighed.
30 grams of chitin were yielded by 50 grams of chitin.
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THE FILTER PROCESS
20 g of activated charcoal, 5 g of chitin, 80 g of sand and 80 g of pebbles were placed in
coffee filters which were shaped like cones were placed funnels and secured in tripods.
Afterwards, the assigned 500 mL samples for testing will be poured through the filters to another
basin separately then the three samples will be subjected to the three tests to monitor changes the
samples.
Afterwards, 10g of potassium aluminum sulfate (alum or tawas) will be added to each of
the 500mL mixtures and, it will then be stirred and left for 60 minutes. The water will then be
decanted to remove any settled substance at the bottom.
TESTING
A. Chemical Testing
The 500mL samples from each location will be sent to a laboratory to analyze for the lead
content of the water samples. An AAS (Atomic Absorption Spectrophotometer) was used to
measure the concentrations of lead in the water samples. Furthermore, additional factors were
tested and measured particularly, the averages and standard deviations of nitrate, nitrite and
ammonium, and phosphate concentrations.
B.Physical Testing
Aside from the laboratory tests, the samples will be subjected to three tests in order to
determine the quality of the water samples. They will be tested before, in-between (after the
pouring through the filter), and after the purification process.
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If you spill acid or base on the lab bench top or on the floor, treat it immediately. If it is
an acid, first neutralize it with baking soda. If it's a base, you can neutralize it with some vinegar,
which is dilute acetic acid. In any case, clean up the area thoroughly after it has been neutralized.
One must also be careful with handling laboratory equipment since these are usually
made of glass. Use glassware that is without defect and has smooth edges. Glassware should
have no cracks, chips, or scratches. In particular, be wary of star cracks that can form on the
bottom of beakers and flasks. Any glassware with such cracks should be properly disposed of
immediately.
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Chapter IV
RESULTS AND DISCUSSION
A. Chemical Testing
These are the results of the chemical tests which were performed on the water samples
before and after they were poured through the filters. Concentrations for the first table are
measured in micromolar (M), while the unit of milligrams per liter (mg/L) is used in the second
table.
Lead Concentrations
Location of Sample Before Treatment After Treatment Percentage ofRemoval
Coast 0.735 mg/L 0.694 mg/L - 5.58 %
Off-shore 0.583 mg/L 0.531 mg/L - 8.92 %
Deep shore 0.534 mg/L 0.487 mg/L - 8.80 %
Dissolved Inorganic Nitrogen, Nitrite and Ammonium, and Phosphates
Sample Nitrate
Nitrite and
Ammonium Phosphates
Before
Average 0.10 M 8.00 M 0.92 M
Standard Deviation 0.16 M 1.35 M 0.34 M
After
Average 0.11 M 7.82 M 0.90 M
Standard Deviation 0.14 M 1.23 M 0.31 M
As seen in the data illustrated above, the lead concentrations of the samples decreased by
a significant amount in all of the samples. Additionally, the nitrate is the only factor which
increased in its value among the variables and the standard deviation decreased, which means the
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values became more consistent. However, the other variables did not change as drastically as the
nitrite content of the samples.
B.Physical Testing
These are the results of the physical tests performed on the water samples. For the
samples tested before the treatment, the average pH was calculated from the three trials to be
compared:
pH Test
Location of Sample Before Treatment After Treatment
Coast 6.33 4
Off-shore 7.67 4
Deep shore 6.00 4
Temperature Test
Sample Trial 1 Trial 2 Trial 3Coast 28.3C 27.8C 28.3C
Off-shore 28.9C 27.8C 30.0C
Deep shore 28.7C 28.3C 27.2C
The results show a drastic change in the pH of the samples, which all became acidic after
the exposure of the water samples to the treatment process. On the other hand, the temperature
readings show that the offshore part of the bay is generally warmer in comparison to the other
parts of the bay.
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Other observations
When filtering the water samples through the filter processes, the resulting water seemed
to be hazy compared to that of the original samples, especially after they were poured through
the sand. Furthermore, the chitin after the acid treatment became more brittle, and had a less
vibrant orange color compared to normal crab shells. Furthermore,
Analysis of Data
Chemical Tests
The results show that chitin and potassium alum are effective in the removal of lead
concentrations in the water. In general it showed a decrease in the concentrations ranging from
approximately 5-9%. Despite having the highest concentration of lead, the water from the coast
reduced the least percentage of contaminants out of the three areas.
As seen in the graph, the overall trend of the lead concentrations as the depth increases is
clearly lower. As it was stated in Chapter II, chitin was mentioned to have good complexation
properties especially with transition and post-transition metals. Furthermore, lead, being a metal,
Coast Offshore Deep shore
Before 0.735 0.583 0.534
After 0.694 0.531 0.487
0
0.1
0.2
0.3
0.4
0.5
0.6
0.7
0.8
Concentrations(inmg/L)
Lead Content of Water
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means that it has high electronegativity. Consequently, this means that it will gain electrons more
easily, and because of this electronegativity, lead will have a greater attraction towards the chitin,
and the complexation and adsorption properties of chitin contributed to the further removal of the
lead content of the water samples. Furthermore, the potassium alum helped by bonding the
impurities, with the lead and settled them at the bottom.
The factors of nitrate, nitrite and ammonium, and phosphates were measured in order to
determine the condition of the bay at the time of the collections. According to Mr. Garcia, the
data suggested that Manila bay was highly eutrophicated and was due to the high concentration
of nitrogen in the bay. This might be due to the fact that Manila bay is highly polluted, with not
just lead, and the pollution consequently caused it to get too much nutrients. After the treatment,
along with the reduction of the lead content, the contaminants also decreased but only in small
amounts.
Physical Tests
In terms of the pH, the samples clearly became more acidic after the water samples were
treated. In chapter II, it was mentioned that one of the solutions that companies use to remove
metals was by changing the pH of the solution and precipitating out the metal after treating it
with other chemical. The changes the chitin brought onto the pH of the samples combined with
the properties of the potassium alum in treating the water, seemed to have contributed in
reducing the lead content of the samples.
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On the other hand, in comparison to the other areas of the bay, the offshore part was seen
to have the highest temperature in general among the areas tested. For this, many factors could
have affected how the temperature behaved, especially current weather patterns, and other
outside factors which can change the temperature of the water before the collection process. The
reason why the temperature is not collected for samples after exposure to the filter process is that
by that time, the temperature will already be controlled and will no longer exhibit readings that
reflect Manila bay in its natural state.
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In the results given, the concentration of lead decreases as the depth increases. In the
findings, the offshore showed the greatest percentage of reduction of contaminants. Along with
all the other data given in the experiment, the researchers conclude that chitin and potassium
alum are both feasible ways to reduce the lead content of seawater, particularly that of Manila
Bay.
Recommendations
For the filter process, it is recommended to have three trials as well to be able to properly
compare the data received. Only one sample per location was used because of the lack of time
and the availability of the testing center could not allow the researchers to do so. Furthermore, if
one is only focused on getting the lead content of the water, it is optional to get the data for
nitrate, nitrite and ammonium, and phosphate content, one may use it if he/she wants to relate the
conditions of the pollution of the water to the metal concentration.
Since chitin and potassium alum were proven to be able to reduce the lead contaminant in
this study, more research should be given in finding other feasible materials which are suitable
for removing heavy metal contaminants (e.g. tilapia scales).
Finally, future experiments should also be done for other metals like cadmium, zinc,
chromium, etc. in order to determine if chitin and potassium alum will become feasible in
removing such metal contaminants.
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