This kit employs two typical quantitative chemical test methods:
colorimetric comparison with standards of known value or titration of the
sample with solutions of known value. The reagent systems employed in
these testing sets can also be used to make simple qualitative tests where the
presence or absence (not the amount) of the factor being investigated is of
concern to the investigator. These qualitative tests can be conducted in the
field or in the classroom where the overhead projector can be used to project
the colorful reactions.
The colorimetric comparison outfits provide color standards of known
values. If the color of the test sample does not match the color of one of the
standards, but is between two color standards, the value assigned to the test
sample is the midpoint between the two standards that bracket the color of
the sample. For example, if the color of the test sample is between the colors
of 0.2 and 0.6 ppm, the result is read as 0.4 ppm. In the pH test, if the color
of the sample is between pH 7.6 and 7.8, the result is read as pH 7.7. When
the color of the test sample (other than pH) is greater than the standard of
the highest value, the test is repeated on a portion of the test sample that has
been diluted on a one-to-one ratio with distilled water . The values of the
color standards are multiplied by a factor of 2 to compensate for the dilution.
Dilutions of higher ratio can be made; however, it must be remembered that
the values of the standards must be multiplied by the ratio of the dilution. A
dilution procedure cannot be used when measuring pH.
The titration procedures are performed using a Direct Reading Titrator
which accurately measures the amount of titration reagent used. Carefully
read the enclosed instruction manual on the Direct Reading Titrator before
performing any of the titrations.
5
Alkalinity Test
The normal conditi ons of the alkalini ty of natural waters are associated with
the carbon dioxide, bicarbonate, carbonate and hydroxide components.
These factors are characteristic of the source of water and the natural
processes taking place at any given time. For particular industrial and
domestic use, it is often desirable to change these characteristics by
treatments such as aeration, neutralization, softening, etc. The particular
treatment and the extent to which it is employed will depend upon the end
use of the water .
Alkalinity of a water is determined by titration with a standard acid to
successive indicator endpoints, thus permitting the calculation of the various
forms of alkalinity.
Field T est Method
QuantityContentsCode
15 mLTotal Alkalinity Indicator2786-E
100Phenolphthalein TabletsT-2246-J
30 mL*Alkalinity Titration Reagent B*4493-G
1Test Tube, 5-10-15 mL, glass, w/cap0778
1Direct Reading Titrator, 0-200 Range0382
WARNING: Reagents marked with a * are considered to be potential health hazards.
To view or print a Material Safety Data Sheet (MSDS) for these reagents see MSDS CD
or www.lamotte.com. To obtain a printed copy, contact LaMotte by email , phone or fax.
The alkalinity titration tube is calibrated so that the result can be read
directly from the scale on the titrator in ppm calcium carbonate (CaCO
The result can be translated to grains per gallon by multiplying the reading
by the factor 0.0585.
Read the LaMotte Direct Reading Titrator Manual before prceeding.
).
3
6
Procedure
1. Fill the test tube (0778) to the 5.0 mL line with the sample water.
2. Add one Phenolphthalein Table (T -2246). Cap and mix until the tablet
is disintegrated. If no red color develops, the “P” Alkalinity is zero. If the
“P” Alkalinity is zero, go to Step 5.
3. Fill the Direct Reading Titrator (0382) with *Alkalinity Titration
Reagent B (4493).
4. Insert the titrator tip into the test tube cap. Slowly add *Alkalinity
T itration Reagent B (4493) while swirling to mix, until the red color
disappears. Read the test result directly from the scale where the large
ring on the Titrator meets the T itrator barrel. This is the “P” or
Phenolphthalein Alkalinity. (Do not refill the Titrator for Step 6.)
5. Remove the cap and add 3 drops of Total Alkalinity Indicator (2786) to
the test sample. Replace the cap and swirl the tube to mix the indicator
with the sample.
6. Continue to add the *Alkalinity Titration Reagent B (4493) with
mixing until the color of the sample changes from greenish blue to a
definite pink color. This is the “T” or Total Alkalinity reading, also know
as the “M” Alkalinity.
7
Calculation of Alkalinity Relationships
The results obtained from the phenolphthalein and total alkalinity
determination offer a means for the stoichiometric classification of the three
principal forms of alkalinity present in many water supplies. The
classification ascribes the entire alkalinity to bicarbonate, carbonate, and
hydroxide; and assumes the absence of other weak acids of inorganic or
organic composition, such as silicic, phosphoric, and boric. This
classification system further presupposes the incompatibility of hydroxide
and bicarbonate alkalinities in the same sample. Since the calculations are
on a stoichiometric basis, ion concentrations in the strictest sense are not
represented in the results.
Carbonate alkalinity is present when the phenolphthalein alkalinity is not
zero but is less than the total alkalinity.
Hydroxide alkalinity is present if the phenolphthalein alkalinity is more than
one-half the total alkalinity .
Bicarbonate alkalinity is present if the phenolphthalein alkalinity is less than
one-half the total alkalinity .
The mathematical conversion of the results is shown in the following table:
Relationships Between Phenolphthalein Alkalinity, Total Alkalinity ,
Carbonate Alkalinity, And Hydroxide Alkalinity:
WARNING: Reagents marked with a * are considered to be potential health hazards.
To view or print a Material Safety Data Sheet (MSDS) for these reagents see MSDS CD
or www.lamotte.com. To obtain a printed copy, contact LaMotte by email , phone or fax.
Read the LaMotte Direct Reading Titrator Manual before proceeding.
Procedure
1. Place the demonstration stage (1038) on the overhead projector and
turn on the projector light.
2. Fill the test tube (0778) to the 10 mL line with sample water and transfer
to a cell on the demonstration stage (1038). (A second cell can be filled
with an identical amount of water sample to be used as a “before” color
standard. Add the indicator in Step 3, but do not titrate.)
3. Add three drops of Total Alkalinity Indicator (2786) and gently stir the
contents of the cell with spatula (0691). If there is any alkalinity present,
a blue-green color will appear.
4. Fill the Direct Reading Titrator (0381) with *Alkalinity Titration
Reagent B (4493).
5. The titrator is held by hand over the cell. Discharge one drop of the
reagent at a time. Stir the mixture after each addition of the titration
solution.
6. When the color of the liquid in the cell changes permanently to pink,
read the test result directly from the scale where the large ring on the
T i trator meets the Titrator barrel. Each minor division equals 2 ppm
CaCO
“P” Alkalinity, use the procedure described in the field test method on
Alkalinity . This value is the “T” Alkalinity . To determine the
3
page 6.
9
Ammonia Nitrogen Test
Ammonia nitrogen is present in variable concentrations in many surface and
ground waters, however, any sudden change in the analysis of a supply which
has been rather constant composition is cause for suspicion. A product of
microbiological activity, ammonia nitrogen is sometimes accepted as
chemical evidence of sanitary pollution when encountered in raw surface
waters.
Ammonia in water is detected by means of *Nessler’s Reagent (4798) which
reacts with ammonia to form a yellow color. The amount of color developed
is directly proportional to the amount of ammonia present.
Field T est Method
QuantityContentsCode
30 mLAmmonia Nitrogen Reagent #14797WT-G
30 mL*Ammonia Nitrogen Reagent #2*4798WT-G
1Test Tube, 5.0 mL, w/cap0230
1Ammonia Nitrogen Comparator,
1.0 and 5.0 ppm
WARNING: Reagents marked with a * are considered to be potential health hazards.
To view or print a Material Safety Data Sheet (MSDS) for these reagents see MSDS CD
or www.lamotte.com. To obtain a printed copy, contact LaMotte by email , phone or fax.
Procedure
1. Fill the test tube (0230) to the 5.0 mL line with sample water .
2. Add 4 drops of Ammonia Nitrogen Reagent #1 (4797). Cap and mix.
3. Add 8 drops of *Ammonia Nitrogen Reagent #2 (4798). Cap and mix.
4. Insert test tube into the Ammonia Nitrogen Comparator (7471). Match
sample color to a color standard. Record as ppm Ammonia Nitrogen.
7471
10
Overhead Projection Demonstration
QuantityContentsCode
30 mLAmmonia Nitrogen Reagent #14797WT-G
30 mL*Ammonia Nitrogen Reagent #2*4798WT-G
1Test Tube, 5.0 mL, w/cap0230
1Demonstration Stage, six cell1038-P
1Spatula6091
WARNING: Reagents marked with a * are considered to be potential health hazards.
To view or print a Material Safety Data Sheet (MSDS) for these reagents see MSDS CD
or www.lamotte.com. To obtain a printed copy, contact LaMotte by email , phone or fax.
Procedure
1. Place the demonstration stage (1038) on the overhead projector and
turn on the projector light.
2. Fill test tube (0230) to the 5 mL line with sample water and transfer to a
cell on the demonstration stage (1038). (As a control, measure 5.0 mL of
sample water and add this to a second cell on the stage. Do not add any
reagents to the control sample.)
3. Add two drops of Ammonia Nitrogen Reagent #1 (4797) and gently stir
with a clean spatula (6091).
4. Add eight drops of *Ammonia Nitrogen Reagent #2 (4798). Mix by
stirring with the spatula.
5. If ammonia is present, a yellow color will form. High concentrations of
ammonia will produce a full yellow color. Lower concentrations will
produce varying shades of yellow and a faint yellow tint will indicate the
presence of a trace quantity of ammonia.
11
Calcium, Magnesium, & Total Hardness Test
Calcium, magnesium and total hardness factors of a water should be
considered as a group since the total hardness of a water generally represents
the total concentration of calcium and magnesium ions expressed as calcium
carbonate. Other ions may contribute to the hardness of water, but in natural
waters all but calcium and magnesium are present in insignificant quantities.
When the hardness of a water is greater than the sum of the carbonate and
bicarbonate alkalinity, the amount in excess is called “noncarbonate
hardness” and such waters may contain considerable amounts of chloride
and sulfate ions. This is an important factor to consider when treating
potable water by ion exchange methods. The hardness of water may range
from zero to hundreds of milligrams per liter, (or parts per million),
depending on the source or the treatment to which it has been subjected.
A knowledge of the hardness of water is of great importance in the industrial
uses since it is the chief source of scale in heat exchange equipment, boilers,
pipe lines, etc. From the domestic standpoint, hard water consumes
excessive quantities of soap, forming curds and depositing a film on hair,
fabrics and glassware.
Total Hardness of water is determined by titration with a EDTA solution,
using Calmagite as the endpoint indicator. The total hardness minus the
calcium hardness equals the magnesium hardness. Calcium is determined by
EDT A titration in a manner similar to the total hardness determination.
Drinking water quality standards, as determined by the US Public Health
Service, set limits of calcium hardness at 200 ppm and magnesium hardness
at 150 ppm. Waters with a total hardness in the range of 0-60 ppm are
termed soft; from 60-120 ppm medium hard, from 120-180 ppm hard and
above 180 ppm very hard.
WARNING: Reagents marked with a * are considered to be potential health hazards.
To view or print a Material Safety Data Sheet (MSDS) for these reagents see MSDS CD
or www.lamotte.com. To obtain a printed copy, contact LaMotte by email , phone or fax.
The Hardness DR Titration Tube (0608) is calibrated so that the hardness
can be read directly from the scale on the Direct Reading Titrator in ppm.
Each minor division on this scale is equal to 4 ppm. Divide this direct
reading by the factor 17.1 to obtain hardness in grains per gallon (gpg).
Read the LaMotte Direct Reading Titrator Manual before proceeding.
Procedure
1. Fill the test tube (0608) to the 12.9 mL line with sample water .
2. Add 5 drops of *Hardness Reagent #5 (4483) and mix. Add 1 Hardness
Reagent #6 Tablet (4484) and swirl to disintegrate the tablet. A red color
will develop.
3. Fill the Direct Reading Titrator (0382) with the Hardness Reagent #7
(4487).
4. Add Hardness Reagent #7 (4487) one drop at a time, swirling to mix
after each drop, until the red color changes to clear blue.
5. Read the test result directly from the scale where the large ring on the
T i trator meets the Titrator barrel. Record as Total Hardness as ppm
Calcium Carbonate.
13
Field T est Method—Calcium Hardness
Procedure
1. Fill the test tube (0769) to the 12.9 ml line with the sample water.
2. Add six drops of *Sodium Hydroxide Reagent with Metal Inhibitors
(4259).
3. Add one Calcium Hardness Indicator Tablet (5250). Cap and mix until
tablet is disintegrated. A red color will appear if calcium is present.
4. Hardness Reagent #7 (4487) is added as described in the Field Test
Method for Total Hardness, until the red color changes to blue. The
results are read as Calcium Hardness in ppm CaCO
5. The Magnesium Hardness level is determined by subtracting the
.
3
Calcium Hardness level from the Total Hardness level.
14
Overhead Projection Demonstration
QuantityContentsCode
100Hardness Reagent #6 Tablets4484-J
15 mL*Hardness Reagent #5*4483-E
15 mL*Sodium Hydroxide Reagent
w/Metal Inhibitors
50Calcium Indicator TabletsT-5250-H
30 mLHardness Reagent #74487DR-G
1Test Tube, 12.9 mL, w/cap0608
1Direct Reading Titrator, 0-200 Range0382
1Demonstration Stage, six cell1038-P
1Spatula0691
WARNING: Reagents marked with a * are considered to be potential health hazards.
To view or print a Material Safety Data Sheet (MSDS) for these reagents see MSDS CD
or www.lamotte.com. To obtain a printed copy, contact LaMotte by email , phone or fax.
*4259-E
Read the LaMotte Direct Reading Titrator Manual before proceeding.
Procedure
1. Place the demonstration stage (1038) on the overhead projector and
turn on the projector light.
2. Fill the test tube (0608) to the 12.9 mL line with sample water and
transfer to a cell on the demonstration stage (1038). Repeat this
operation so that four cells of the demonstration stage are filled. One cell
will be used for the Total Hardness test, one cell will be used for the
Calcium Hardness test and the other two cells will be used as controls.
Number the cells 1, 2, 3 and 4.
3. T o cells 1 and 2, add 5 drops of *Hardness Reagent #5 (4483) and mix.
Add 1 Hardness Reagent #6 Tablet (4484) and swirl until tablet is
disintegrated. A red color will develop.
4. Fill the Direct Reading Titrator (0382) with the Hardness Reagent #7
(4487). Add one drop at a time to cell 2 until the sample color changes
from red to clear blue. Stir the sample after the addition of each drop.
Read the test result directly from the scale where the large ring on the
T i trator meets the Titrator barrel. Record the result as ppm Total
Hardness.
15
5. T o cells 3 and 4, add six drops of *Sodium Hydroxide Reagent with
Metal Inhibitors (4259) and stir the contents of the cells with the
spatula.
6. T o cells 3 and 4, add one Calcium Hardness Indicator Tablet (5250) to
each and stir until tablets are disintegrated or until the liquid has
developed a full red color. Cell 3 will be used as the “before” color change
standard.
7. Refill the Direct Reading Titrator with Hardness Reagent #7 and add
dropwise to cell 4, stirring the solution after each drop. Continue until
the sample color changes from red to blue. Read the test result directly
from the scale where the large ring on the Titrator meets the Titrator
barrel. Record the result as ppm Calcium Hardness.
8. Subtract the Calcium Hardness level from the Total Hardness level to
determine the Magnesium Hardness level.
16
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