Materials and Equipment
Research Instrument
The researchers used a questionnaire as an initial action to assess the water potability of
water within the chosen locations. Water collection and sampling were commenced in which
samples obtained were then subjected to analysis wherein the presence of physicochemical and
coliforms from the water tanks of each purok in Don Salvador Benedicto was determined. The
physicochemical test and coliform test were performed in a separate laboratory. The
questionnaire was divided into three categories: Water consumption, water tank management,
and related health issues. The questionnaire was based on the study of Dabalos (2020), stating
the questions in the first and second categories. The questions were written in the Hiligaynon
dialect for easier understanding for the people in the barangay to answer.
The following materials and equipment were utilized:
Questionnaire. A valid material that was used for the evaluation of the water quality in
connection to the current health of the residents. Included in this item are the assessment
concerning water consumption, the management of the tank in the designated area, and the health
issues that could be related to the utilization of water within the area.
Ethical Consideration
This study underwent special consideration with the respondents as to the result of the study
being obtained. The result of the quality of this study was confidential by any means, the
information is made available or accessed by anyone but the people who are involved in this
study. The respondents participating in this evaluation are fully informed about what is being
conducted. They are aware of the purpose of the study; hence, they can decide as to whether they
can participate in the study or not. This study did not do any harm to the purok of the sample
obtained and the respondent who participated in this study. The answer of the respondents is
confidential to follow the Republic Act 10173 (Data privacy act of 2012) which protects the
fundamental right of privacy ensuring the free flow of information (National Privacy
Commission). All the related studies obtained are given proper credit to prevent the plagiarism of
the said study. This study has secured permission through a letter sent to the Ethics committee.
Permits were secured to conduct the study in the barangay through a letter given to the Barangay
captain and the heads of the Puroks.
Procedures
This section of the paper exhibits the techniques used in the collection for the analysis.
Included here are the two parameters and their specific methods for examination.
Data gathering
Interview Procedure. Interviews were conducted on each purok to secure permission on
survey and water sample collection. The water tanks were discussed and the water sources of the
residents in each purok. The number of households to be surveyed were also discussed and the
kind of livelihood the residents have. Permission letters were given to each purok to formally
conduct the survey and the water sample collection.
Water sample collection. The tank water sample was collected in Purok Agbalasyang,
Purok Magasin, and Purok Tayao. One liter of water samples from the tanks was utilized for
each microbiological and physio-chemical test.
Water sampling. One (1) liter water sample per tank was collected for both physicochemical
testing and coliform. A total of 3.05L of water samples was collected from each tank. In
addition, a total of 3.15L of water samples were collected from the sampling site. The sample
was delivered immediately to the laboratory for testing.
Sampling procedure. The gathering of samples was done by using sanitized bottles and
hands. The sample collection was based on a closed tank gathering procedure.
The sample was collected in a sterile bottle. 2-5 minutes were allotted for the pipe or the
hose of the tank to flow. The opening was disinfected before collection. The sample bottle for
total coliform was filled leaving a ¼ space before the opening.
Furthermore, the use of a faucet attached to the tank for sampling was done by wiping the
outlet first and then cleaning the spout. By opening the spout with maximum flow for 1-2
minutes it clears the service line. The spout was then sterilized with a portable lighter for metal
and hypochlorite or alcohol wipes for plastic. Water was then opened for 1-2 minutes at normal
rate flow, which is then gathered through a sterilized bottle filling until the shoulder of the bottle,
was covered, and transported. (World Health Organization, 2011)
Transport procedure. A sterile, tightly closed, and sealed container served as a medium
for transport. The collected water samples were kept in a clean cooler having temperatures
between 4 and 6 degrees Celsius to aid contaminants from breaking down during transport. After
collection, water samples were immediately delivered to the laboratory for testing.
Water potability analysis. A total of nine (9) samples were obtained from the site and
transported immediately to Negros Prawn Producers Cooperative. These samples were subjected
to coliform detection and physiochemical tests.
Physio-Chemical Test
Test for Color. The colorimetric method was performed to determine the color of water
samples. Water samples were placed in clean glassware. Color determination was performed
within a reasonable period due to possible physical or biological changes that may affect the
color. Sample color was observed by filling a 50 ml Nessler tube and comparison was done to a
standard. Observation through looking vertically downward through tubes in an angle at which
light is being reflected upward. Dilution of samples with distilled samples in proportions until
their color is in the range of standard (American Public Health Association, 2018).
American Public Health Association. (2018). Standard Methods for the Examination of Water
and Wastewater. Standard Method. Retrieved March 15, 2024, from
https://www.standardmethods.org/doi/full/10.2105/SMWW.2882.017?role=tab
Test for Dissolved Solid. Water samples were placed in transparent bottles and not filled
to mix efficiently by shaking the bottle. Analyzing of samples were examined preferably within
4 hours or as much as possible. As for the procedure, the evaporating dish was dried in the oven
for 1 hour at 180 degrees Celsius and cooled in a desiccator and weighed. Glass-fiber filter disk
was placed in the filtration apparatus. Three successive 20 ml pure water was placed in a vacuum
and wash disk. A known volume of the sample was placed on a filtration apparatus. The vacuum
and transfer filtrate were placed on a weighted and clean evaporated dish. The evaporating dish
is placed in an oven for an hour at 180 degrees Celsius then, it is cooled in a desiccator and was
then weighed. Dry again and weighted to a constant weight (APPENDIX-2 STANDARD
OPERATING PROCEDURES OF WATER QUALITY ANALYSIS, n.d.). Calculation of
results with the use of a formula of TDS (mg/l) = (A (mg) - B(mg)) x 1000/ V (ml) with an
acceptable value provided by Negros Prawn Producers Cooperative Laboratory of 600 TDS as
contaminated with dissolved solids.
Test for Turbidity. The turbidity of the sample was assessed by inserting it within a
transparency tube to evaluate the water’s purity (Peterson & Gunderson, 2008). The water
samples were collected in either plastic or glass bottles. Additionally, according to Ma et al.
(2020). Precisely, the weight of the original residue was calculated using a digital balance, and
the final weight is recorded after the filtering procedure.
Test for pH. The water is properly stirred and mixed with a stirring rod. A water sample
of about 40 ml is added to a beaker and its temperature is on standby for one hour for it to be
stabilized. After one hour, the temperature was measured and adjusted in the pH meter. Standard
solutions are utilized to standardize the pH meter. The electrodes were placed in the solution for
about 30 seconds before starting the reading. Once the reading is shown, it must be on to the
nearest tenth of the whole number. (Water Supply Archives, 2021).
Test for Chloride. The chloride water was identified using the Mohr method. Using
potassium chromate, the collected water is titrated to a silver nitrate solution. A white precipitate
of silver chloride would form at the bottom of the flask as silver nitrate solution is gradually
poured into it. When all of the chloride ions have reacted and precipitated, the titration has
reached its endpoint (Tasrik, 2015).
Test for Total hardness. Selection of sample that the volume itself requires less than 15
mL EDTA titrant and complete titration must be within 5 minutes from time of adding the
buffer. Dilute 25 mL sample to a 50 mL with distilled water in a porcelain casserole or any other
suitable vessel. Next, is to add a 1 to 2 mL buffer solution. Add 1 to 2 drops of indicator solution
or an appropriate amount of dry-powder indicator formulation. EDTA titrant will be added
slowly, with continuous stirring, until the last reddish tinge disappears. Endpoint results normally
have a blue result (2340 HARDNESS, 2018).
Test for Iron. Iron is placed into a solution and is reduced to a ferrous state by boiling
with acid and hydroxylamine, which is then treated with 1,10-phenanthroline at pH 3.2 to 3.3.
Each atom of the ferrous iron is chelated by the three molecules of phenanthroline to form an
orange-red complex. The colored solution obeys Beer's law with its intensity of pH from 3 to 9
and a pH of 2.9 to 3.5 insure rapid color development in the presence of excess phenanthroline.
Negros Prawn Producers Laboratory indicates an acceptable value of 1.0 mg/L (3500-Fe IRON,
2018).
Test for Nitrate. The sample was passed through an ion exchange column and combined
with an effluent consisting of nitrate (NO3). Nitrate was created as a blank and a suitable
standard solution by combining it with distilled water. The sample, blank, and standard solutions
were then each given a separate series of reagent additions. After being filled with hydrazine
sulfate solution, the flasks are heated in a water bath at a constant boil for five minutes. Reagents
are then added after cooling for two minutes in flasks which have been moved to an ice bath.
After 15 minutes, retrieval from the ice water is made for the color to fully develop. The process
is based on hydrazine-mediated conversion of nitrate to nitrite in a heated alkaline solution,
followed by the diazotization of the nitrite thus produced and the interaction with the compound
of diazo with 1-naphthyl ethylenediamine to produce a strongly colored red dye (Fishman et al.,
1964).
Test for Nitrite. Diazotization Method is based on the reaction between aromatic
primary amine (-NH2) HONO, in presence of excess mineral and organic acids. Sodium nitrite is
used as a direct method of diazotization. It gives Hydrogen nitrite in acidic solution. Many
aromatic amines with free -NH2 are analyzed quantitatively by measuring the volume of sodium
nitrite solution required to convert them into diazonium salt. When all aromatic amine has
reacted with sodium nitrite, the next portion (excess of NaNO2) is added to the solution under
the test, converted to HONO that remains in the solution and can be detected by starch paper or
paste as an external indicator. The liberated iodine reacts with starch and gives blue color. The
diazotization proceeds quantitatively only in the presence of inorganic acid. It is important to
check the acidity of the titration. If there is no excess acid present, starch iodide will not detect
excess hydrogen nitrite and so will not indicate the end point (Chang, et.al., 2020)
Test for Odor. Water samples were collected in glass bottles and tested as soon as
possible. Collection of at least 500 mL of sample were filled to the top to ensure that no
extraneous odors are to be drawn in the sample as it cools (NEMI Method Summary - 2150 B,
2005). The odor was evaluated at either 40 degrees Celsius or 60 degrees Celsius.
Test for Sulfate. Sulfate ion is precipitated in an acetic acid medium with barium
chloride (BaCI) to generate uniformly sized barium sulfate (BaSO.) crystals. Perform a Barium
sulfate turbidity formation by adding BaCk and crystals and stir at a constant speed for 60s. After
the stirring period has ended, pour the solution into the photometer's absorption cell, and
measure the turbidity at 5 + 0.5 minutes. Estimate the sulfate concentration in a sample using sa
calibration curve preparation. After the calibration, run blanks with no BaCk to correct for
sample color and turbidity (Achio, 2015).
Total Coliform Detection
Coliform detection. Each sample was labelled, received, and processed in the laboratory.
The sample testing for coliform determination is no later than 24 hours after the collection (Bolo
et al., 2021). All samples were processed using the Multiple Tube Fermentation Technique
(MTFT). The results were in comparison to the Most Probable Number (MPN) of coliform level.
Test for Coliforms. The process known as Heterotrophic Plate Counts (HPC), which
employs the spread plate technique, was used to estimate the number of bacteria in a sample. The
HPC plate was inoculated according to the standard procedure using agar. The inoculum was
transferred from the sample to the agar surface close to the center and hand distributed.
Following this, it is then observed and counted.
Data analysis
The data was obtained from the survey, and the test results of two parameters were
gathered and analyzed descriptively through the portion of the population that obtains drinking
water from the tank. The statistical tool of central tendency is used to determine the mean,
frequency distribution and percentage of households that obtain water from the tank.
The level of water potability of the following puroks of Barangay Bago, Don Salvador
Benedicto was based on the parameters - physicochemical test and total coliform test. The
physicochemical parameters include color, total dissolved units, turbidity, pH, chloride, total
hardness, iron, nitrate, nitrite, sulfate and odor which is measured through Visual Comparison
Method, Total Dissolved Solids dried at 180 degrees Celsius, Nephelometric Method,
Electrometric Method (4500-H+ B), Argentometric Method 4500-Cl-B, Titrimetric Method
(2350C), Phenanthroline Method-350-Fe B, Spectrophotometric Method, Diazotization Method,
Turbidimetric Method 4500-SO4 E and Threshold Odor Test, respectively. The coliform test was
analyzed using Multi Tube Fermentation Technique for both total coliform and thermotolerant
coliform, and the 9215 C Spread Plate Method for heterotrophic plate count.
The physical characteristics of water samples and the health-related concerns of the
population are analyzed from the data obtained from a valid and reliable questionnaire by
measuring the central tendencies. The quality of water was verified by comparing the results of
total coliform and physicochemical parameters to the Philippine National Standards for Drinking
Water.
Chapter 3
RESULTS, DISCUSSION, AND IMPLICATIONS
The study aimed to determine the quality of water being consumed in the 3 Puroks,
Agbalasyang, Magasin, and Tayao. This study employed a descriptive method for the analysis of
data. Survey questionnaires were given to each household in the mentioned puroks, to correlate
with the results that were analyzed. Visual presentations of the data collected from the
questionnaire were utilized, such as bar graphs and pie charts. The parameters used in the study
are total coliform and physicochemical.
Results and Discussion
Survey Results
The following are the survey outcomes based on the responses of the participants.
These are divided into three (3) parts which are water consumption, and health-related issues.
The Statistical tool of Central Tendency was utilized for a probability distribution of physical
characteristics among three (3) puroks
Procedure part
Water sampling. One (1) liter water sample per tank was collected for both
physicochemical testing and coliform. A total of 3.05L of water samples was collected from each
tank. In addition, a total of 3.15L of water samples were collected from the sampling site. The
sample was delivered immediately to the laboratory for testing.