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Water and Wastewater Engineering - Sciences Club

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7-10 WATER AND WASTEWATER ENGINEERING<br />

protonated anion species are common. In addition, the cations or anions may form complexes with<br />

other materials in solution, thus, reducing their effective concentration (Sawyer et al., 2003).<br />

Of particular importance is the effect of solution pH on the solubility of cations. For example,<br />

assuming that there are no other compounds in solution to react with calcium hydroxide, the solubility<br />

product would be<br />

or<br />

However, log [OH �<br />

] is a function of pH:<br />

or<br />

S o Equation 7-20 may be written<br />

2� � 2<br />

Ksp � [Ca ][OH ]<br />

2�<br />

�<br />

sp<br />

log [ Ca ] �log K �2log<br />

[ OH ]<br />

�<br />

w w [ ]<br />

pH �pK �pOH �pK �log<br />

OH<br />

log [ OH ] pH p<br />

� � � Kw (7-19)<br />

(7-20)<br />

(7-21)<br />

(7-22)<br />

2�<br />

log [ Ca ] �log Ksp�2( pH �pKw)<br />

(7-23)<br />

The pH not only affects the solubility of metal hydroxides, it also affects other equilibria,<br />

which in turn affects the solubility of the cation. Of particular importance is the relationship of<br />

the carbonate buffer system to pH. As noted in Equations 6-5 <strong>and</strong> 6-6, carbonate is an anion of the<br />

weak diprotic acid, H 2 CO 3 . The carbonate species both influence <strong>and</strong> are influenced by the pH.<br />

The sum of the carbonate species may be specified as a total concentration of inorganic carbon:<br />

� �<br />

CT �[ H CO ] �[ HCO3] �[<br />

CO3<br />

]<br />

2<br />

2 3<br />

(7-24)<br />

2 �<br />

If the pH is specified, the saturation value for [Ca ] can be estimated for a given value of C T .<br />

This is illustrated in Figure 7-6 .<br />

In lime-soda softening, the pH is controlled by the addition of lime. To precipitate CaCO 3 ,<br />

the pH of the water must be raised to about 10.3. To precipitate magnesium, the pH must be<br />

raised to a range of about 11 to 11.3 (Horsley et al., 2005).<br />

Process Limitations <strong>and</strong> Empirical Considerations. Lime-soda softening cannot produce a<br />

water completely free of hardness because of the solubility of CaCO 3 <strong>and</strong> Mg(OH) 2 , the physical<br />

limitations of mixing <strong>and</strong> contact, <strong>and</strong> the lack of sufficient time for the reactions to go to completion.<br />

Thus, the minimum calcium hardness that can be achieved is about 30 mg/L as CaCO 3 ,<br />

<strong>and</strong> the minimum magnesium hardness is about 10 mg/L as CaCO 3 . Because of the slimy condition<br />

that results when soap is used with a water that is too soft, historically the goal for final total<br />

hardness has been set at between 75 <strong>and</strong> 120 mg/L as CaCO 3 . In recent years, many utilities have<br />

raised the target hardness to 120 to 150 mg/L as CaCO 3 to reduce chemical costs <strong>and</strong> residuals *<br />

production (Horsley et al., 2005).<br />

In order to achieve reasonable removal of hardness in a reasonable time period, an extra amount<br />

of Ca(OH) 2 beyond the stoichiometric amount usually is provided. Based on empirical experience, the<br />

minimum extra amount is 20 mg/L of Ca(OH) 2 expressed as CaCO 3 (or 0.40 meq).<br />

*Residuals � precipitate in the lime-softening process <strong>and</strong> brine in ion exchange <strong>and</strong> reverse osmosis softening.

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