Alkalinity or AT
is a measure of the ability of a solution to neutralize
acids to the equivalence point of
carbonate or bicarbonate. Alkalinity is closely related to the acid neutralizing
capacity (ANC) of a solution and ANC is often
incorrectly used to refer to alkalinity. The
alkalinity is equal to the stoichiometric
sum of the bases
in solution. In the natural environment carbonate
alkalinity tends to make up most of the total alkalinity due to the
common occurrence and dissolution of carbonate rocks and
presence of carbon
dioxide in the atmosphere.
Other common natural components that can contribute to alkalinity include borate, hydroxide, phosphate, silicate, nitrate, dissolved ammonia, the conjugate
bases of some organic acids
and sulfide. Solutions
produced in a laboratory may contain a virtually limitless number of bases that
contribute to alkalinity. Alkalinity is usually given in the unit mEq/L (milliequivalent per liter). Commercially, as in the pool industry,
alkalinity might also be given in the unit ppm or parts per million.
Total alkalinity is the measure
of the amount of alkaline buffers
(primarily carbonates and bicarbonates) in your water. These
alkaline substances buffer the water against sudden changes in pH. Total
alkalinity is considered the key to water balance. It is the
first parameter you should balance when making routine adjustments to your
water.
If you neglect to check the total alkalinity in your pool or spa, you may have trouble balancing the pH. You may also notice that pH fluctuates suddenly despite your best efforts to keep it in the ideal range. If the alkalinity is too low, anything introduced to the water will have an immediate impact on pH. Abrupt shifts in pH can cause scaling or corrosion of metal equipment and fixtures as well as other problems. When the total alkalinity is high, the pH has a tendency to drift upward, causing scale to form.
Raw Water:
M-alkalinity as CaCo3 |
mg/l
|
160
|
When the total alkalinity is too
low, add sodium bicarbonate. If the total alkalinity is too
high, you can lower it by using muriatic acid or sodium
bisulfate.
Maintaining an ideal level of alkalinity will protect your pool or spa and its equipment from the harmful effects of sudden pH fluctuations. Think of the alkalinity as training wheels: it keeps the pH in balance without allowing it to tip too far to either side. Of course the pH can still drift upward or downward, but that change will happen gradually as long as the alkalinity falls within the ideal range. The ideal range of total alkalinity for pools and spas is between 80 and 120 ppm (mg/L).
When the total alkalinity is too low, add sodium bicarbonate. If the total alkalinity is too high, you can lower it by using muriatic acid or sodium bisulfate.
For more detailed advice on the specific chemical treatment for your pool or spa, contact your dealer.
Alkalinity is sometimes incorrectly used interchangeably with basicity. For example, the pH of a solution can be lowered by the addition of CO2. This will reduce the basicity; however, the alkalinity will remain unchanged
Theoretical treatment of alkalinity
In typical groundwater or seawater the measured
alkalinity is set equal to:
AT = [HCO3−]T + 2[CO3−2]T + [B(OH)4−]T + [OH−]T + 2[PO4−3]T + [HPO4−2]T + [SiO(OH)3−]T − [H+]sws − [HSO4−]
AT = [HCO3−]T + 2[CO3−2]T + [B(OH)4−]T + [OH−]T + 2[PO4−3]T + [HPO4−2]T + [SiO(OH)3−]T − [H+]sws − [HSO4−]
(Subscript T indicates the total concentration of the species in the solution as measured. This is opposed to the free concentration, which takes into account the significant amount of ion pair interactions that occur in seawater.)
Alkalinity can be measured by titrating a sample with a strong acid until all the buffering capacity of the aforementioned ions above the pH of bicarbonate or carbonate is consumed. This point is functionally set to pH 4.5. At this point, all the bases of interest have been protonated to the zero level species, hence they no longer cause alkalinity. For example, the following reactions take place during the addition of acid to a typical seawater solution:
HCO3−
+ H+ → CO2 + H2O
CO3−2
+ 2H+ → CO2 + H2O
B(OH)4−
+ H+ → B(OH)3 + H2O
OH−
+ H+ → H2O
PO4−3
+ 2H+ → H2PO4−
HPO4−2
+ H+ → H2PO4−
[SiO(OH)3−]
+ H+ → [Si(OH)40]
It can be seen from the above
protonation reactions that most bases consume one
proton (H+) to become a neutral species, thus increasing
alkalinity by one per equivalent. CO3−2 however, will
consume two protons before becoming a zero level
species (CO2), thus it increases alkalinity by two per mole
of CO3−2. [H+] and [HSO4−]
decrease alkalintiy, as they act as sources of protons. They are often
represented collectively as [H+]T.
Alkalinity is typically reported as mg/L as CaCO3. This can be converted into mill Equivalents per Liter (mEq/L) by dividing by 50 (the approximate MW of CaCO3/2).
Alkalinity is typically reported as mg/L as CaCO3. This can be converted into mill Equivalents per Liter (mEq/L) by dividing by 50 (the approximate MW of CaCO3/2).
Example problems
Sum of contributing
species
The following equations demonstrate the relative
contributions of each component to the alkalinity of a typical seawater sample.
Contributions are in μmol.kg−soln-1 and are obtained from
A Handbook of Methods for the analysis
of carbon dioxide parameters in seawater "[1],"(Salinity = 35, pH
= 8.1, Temperature = 25°C).
AT = [HCO3−]T + 2[CO3−2]T + [B(OH)4−]T + [OH−]T + 3[PO4−3]T + [HPO4−2]T + [SiO(OH)3−]T − [H+] − [HSO4−] − [HF]
Phosphates and silicate, being nutrients, are typically negligible. At pH = 8.1 [HSO4−] and [HF] are also negligible. So,
AT = [HCO3-]T + 2[CO3−2]T + [B(OH)4−]T + [OH−]T − [H+]
AT = 1830 + 2*270 + 100 + 10 − 0.01
AT = 2480 μmol.kg−soln-1
AT = [HCO3−]T + 2[CO3−2]T + [B(OH)4−]T + [OH−]T + 3[PO4−3]T + [HPO4−2]T + [SiO(OH)3−]T − [H+] − [HSO4−] − [HF]
Phosphates and silicate, being nutrients, are typically negligible. At pH = 8.1 [HSO4−] and [HF] are also negligible. So,
AT = [HCO3-]T + 2[CO3−2]T + [B(OH)4−]T + [OH−]T − [H+]
AT = 1830 + 2*270 + 100 + 10 − 0.01
AT = 2480 μmol.kg−soln-1
Addition of CO2
The addition (or
removal) of CO2 to a solution does not change the alkalinity.
This is because the net reaction produces the same number of equivalents of
positively contributing species (H+) as negative contributing species (HCO3-
and/or CO3--).
At neutral pH's:
CO2 + H2O → HCO3− + H+
At high pH's:
CO2 + H2O → CO3−2 + 2H+
At neutral pH's:
CO2 + H2O → HCO3− + H+
At high pH's:
CO2 + H2O → CO3−2 + 2H+
Dissolution of
carbonate rock
Addition of CO2 to a solution in contact with a
solid can affect the alkalinity, especially for carbonate minerals in contact
with groundwater or seawater . The dissolution (or precipitation) of carbonate
rock has a strong influence on the alkalinity. This is because carbonate rock
is composed of CaCO3 and its dissociation will add Ca+2
and CO3−2 into solution. Ca+2 will not influence
alkalinity, but CO3−2 will increase alkalinity by 2
units.
P ALKALINITY
Alkalinity in trisodium Phoshate
P alkalinity
V1* 40*N*100/w *1000
W= material of aliquot
N= Normality of HCL
No comments:
Post a Comment