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Acid-Base Chemistry Examples - Civil and Environmental Engineering

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<strong>Acid</strong>-<strong>Base</strong> <strong>Chemistry</strong><br />

Extremely important in the environment<br />

<strong>Examples</strong><br />

• <strong>Acid</strong> rain<br />

• Biological systems<br />

- cells buffer (i.e., stabilize) their internal pH<br />

- biological processes in nature <strong>and</strong> in engineered processes need<br />

stable pH<br />

• Air-water interactions<br />

CO 2 in atmosphere<br />

↑↓<br />

CO 2 in surface waters<br />

↑↓ + H 2 O<br />

H 2 CO 3<br />

↑↓ - H +<br />

HCO 3<br />

-<br />

bicarbonate ion<br />

↑↓ - H +<br />

CO 3<br />

2-<br />

carbonate ion<br />

Thus, adding CO 2 lowers the pH (makes system more acidic)


• <strong>Acid</strong> mine drainage – Coal contains reduced sulfur <strong>and</strong> acid mine<br />

drainage has long been an environmental problem. Much of this<br />

sulfur is contained in pyrite, FeS 2 , a common mineral. On exposure to<br />

the air it oxidizes giving ferric, sulfate <strong>and</strong> hydrogen ions:<br />

FeS 2 + 15/4 O 2 + 1/2 H 2 O ↔ Fe 3+ + 2 SO 4 2- + 2 H +<br />

The ferric ions undergo a hydrolysis reaction with water liberating more<br />

protons (thus making the system even more acidic) <strong>and</strong> precipitating ferric<br />

hydroxide (“rust”) on the stream bottom <strong>and</strong> banks.<br />

Fe 3+ + 3 H 2 O ↔ Fe(OH) 3 (s) + 3 H +<br />

• A treatment question – Most metals (e.g., Fe, Cu, Zn etc) come from<br />

open-pit mines using large equipment for processing. After removal<br />

of the metals from the finely crushed rock the residual “tailings” are<br />

disposed in piles or disposal areas. The residual sulfide will, over<br />

time, oxidize causing the material to become acidic <strong>and</strong> thus leaching<br />

metals into surface <strong>and</strong> ground water. To prevent this potential<br />

contamination, limestone (CaCO 3 ) is added to neutralize the released<br />

hydrogen ions. Can you calculate the amount of limestone that would<br />

have to be added if, for instance, the waste material had been found to<br />

contain 4% S?


Consider the reaction<br />

H 2 O ↔ H + + OH -<br />

<strong>Base</strong>d on the definition of K<br />

+ -<br />

{ H }{ OH }<br />

1000 g<br />

~<br />

K =<br />

⇒ concentration of H 2 O: L<br />

= 55.5 mol/L<br />

18g/mol<br />

{ H O}<br />

2<br />

But<br />

Define {H 2 O} = 1<br />

In a dilute system { } = [ ]<br />

K w = [H + ] [OH - ]<br />

at 25°C, K w = 1.0 × 10 -14<br />

[H + ] [OH - ] = 10 -14<br />

When are they equal? [H + ] = [OH - ] = (10 -14 ) 1/2 = 10 -7<br />

But in an acidified lake<br />

[H + ] = 10 -4 ; [OH - ] = 10 -14 /[H + ] = 10 -14 /10 -4 = 10 -10<br />

Range of concentrations is orders of magnitude.<br />

So – define “p” = “-log 10 ”<br />

pH = -log 10 [H + ]<br />

pOH = -log 10 [OH - ]<br />

So we don’t always have to deal with negative values - if we just use logs<br />

Note the – sign: as [H + ] increases, pH decreases<br />

pH 7 [H + ] = 10 -7 [OH - ] = 10 -7<br />

pH 4 [H + ] = 10 -4 [OH - ] = 10 -10<br />

Convert the equilibrium expression<br />

-log 10 ([H + ] [OH - ]) = -log 10 [H + ] + -log 10 [OH - ] = -log 10 K w<br />

= pK w = -log 10 10 -14 = 14<br />

<strong>and</strong><br />

-log 10 [H + ] + -log 10 [OH - ] = 14<br />

so<br />

pH + pOH =14<br />

It is useful to consider log – log plots of concentration


0<br />

2<br />

log [H + ]<br />

log [OH - ]<br />

4<br />

10 -4<br />

- log C = pC<br />

6<br />

8<br />

10<br />

10 -10<br />

pH 7<br />

[H + ] = [OH - ]<br />

12<br />

14<br />

0 2 4 6 8 10 12 14<br />

pH --- "Master Variable"<br />

We can treat acids <strong>and</strong> bases in a similar manner<br />

Definitions<br />

<strong>Acid</strong> can donate H + (proton)<br />

<strong>Base</strong> can accept H +<br />

Generic acid “HA”<br />

HA ↔ H + + A - (dissociation)<br />

A strong acid (HCl – hydrochloric, HNO 3 – nitric, H 2 SO 4 – sulfuric, but only<br />

first proton) is one for which the dissociation is complete in water<br />

If the dissociation is


We can so the same thing we did for H 2 O:<br />

HA ↔ H + + A -<br />

+ -<br />

[ H ][ A ]<br />

K = = "acidityconstant"<br />

(eqn 1)<br />

a<br />

[ HA]<br />

Example acetic acid CH 3 COOH = “HA”<br />

<strong>and</strong> acetate ion CH 3 COO - = “A - ”<br />

pK a = 4.7, K a = 10 -4.7 = 2.0 × 10 -5<br />

Put 10 -4 mol CH 3 COOH in 1 L solution. What is the pH?<br />

Is this a strong acid?<br />

+<br />

-<br />

5 [ H ][ CH3COO<br />

]<br />

From equation 1: 2×<br />

10<br />

− =<br />

−5<br />

+ 2×<br />

10<br />

<strong>and</strong> [ ]<br />

[ CH3COOH]<br />

H =<br />

-<br />

[ CH3COO<br />

]<br />

[ CH ]<br />

3COOH<br />

we could solve for<br />

-<br />

[ CH COO ]<br />

What else do we know? 10 -4 M!<br />

3<br />

[ CH COOH]<br />

3<br />

but we would still need another equation.<br />

[CH 3 COOH] + [CH 3 COO - ] = 10 -4 = C T (eqn 2)<br />

Combining eqn 1 <strong>and</strong> eqn 2 gives<br />

<strong>and</strong><br />

+<br />

[ HA] [ H ]<br />

=<br />

+<br />

CT<br />

K a + [ H ]<br />

-<br />

[ A ] K a<br />

=<br />

+<br />

CT<br />

K + [ H ]<br />

a<br />

(eqn 3)<br />

(eqn 4)<br />

We will use these instead of solving directly for [H + ]. The two equations<br />

generate a useful graph (see Appendix p 9 for mathematical details).


0<br />

-log C = pC<br />

2<br />

4<br />

6<br />

8<br />

log C T<br />

CH 3<br />

COO -<br />

CH 3<br />

COOH<br />

10<br />

0 2 4<br />

pK a 6 8 10 12 14<br />

pH<br />

This graph shows the concentration of the CH 3 COOH (protonated) species<br />

<strong>and</strong> CH 3 COO - (dissociated) species at any pH. Note that at a low pH, the<br />

protonated species is predominant, but at higher pH, the dissociated species<br />

predominates.<br />

Notice that when the pH equals the pK a , the CH 3 COOH <strong>and</strong> CH 3 COO -<br />

concentrations are equal.<br />

Because a strong acid completely dissociates to A - , the pK a would have to be<br />

very low.<br />

At any pH below 4.7, acetic acid is less than 50% dissociated. It is a weak<br />

acid. A strong acid would have to have a very small pK a . Actually, their<br />

values are negative!<br />

So now we know that acetic acid is a weak acid. But we never figured out<br />

where we were on the log C – pH diagram (i.e., the pH after adding 10 -4 M<br />

acetic acid to the H 2 O).<br />

We need another equation. There are two that can be used, either a charge<br />

balance or a proton condition. In this course we’ll just use the charge<br />

balance which simply says that the total negative charge in the system must<br />

equal the overall positive chare (“electroneutrality”).<br />

We add the concentrations of all anions on one side of the equation, cations<br />

on the other. In our example


[H + ] = [H 3 CCOO - ] + [OH - ]<br />

We finish our problem by combining our acetic acid graph with our previous<br />

graph for [H + ] <strong>and</strong> [OH - ], <strong>and</strong> look for a pH where the [H + ], [H 3 CCOO - ], <strong>and</strong><br />

[OH - ] lines satisfy the above condition.<br />

0<br />

2<br />

4<br />

H +<br />

CH 3<br />

COO -<br />

OH -<br />

-log C = pC<br />

6<br />

8<br />

10<br />

CH 3<br />

COOH<br />

12<br />

14<br />

0 2 4 6 8 10 12 14<br />

pH<br />

You could have plotted -log C as is frequently done. The graph would have<br />

been identical except for the sign of the values on the y-axis. If you draw<br />

the graph by h<strong>and</strong>, you must use graph paper. Preferable is 10 × 10 to the<br />

centimeter (10 × 10 to the inch may also be used).<br />

The solution to the charge balance equation is found by inspection being<br />

careful to consider only the lines of species that are represented in the<br />

electroneutrality equation <strong>and</strong> remembering that the graph shows<br />

logarithmic, not linear, values. The charge balance is fulfilled when pH ≅<br />

4.5, where [CH 3 COO - ] ≅ 10 -4.5 , [H + ] ≅ 10 -4.5 , <strong>and</strong> [OH - ] is so small that it can<br />

be neglected (~10 -9.5 ). So the pH of the acetic acid solution will be 4.5.<br />

So the overall approach is this:<br />

1. Get the pK a . It’s –log 10 K a if you have K a . If you have K b or pK b (the<br />

base dissociation constant), use K b = 10 -14 / K a , or p K b = 14 – p K a .<br />

2. Get C T <strong>and</strong> –log 10 C T (pC T ). C T is the sum of [HA] <strong>and</strong> [A - ] already in<br />

the solution plus the amount added. It must be in moles/L.<br />

3. Draw the graph in the following steps:<br />

a. Draw axes as shown in the example.


. Draw a vertical line at pH = pK a .<br />

c. Draw a horizontal line at –log 10 C T .<br />

d. Locate the intersection from (b) <strong>and</strong> (c) <strong>and</strong> from it, draw lines<br />

downward in each direction at 45°. Also locate a point (x) 0.3<br />

units below this intersection.<br />

e. Draw a line that connects the lower portion of each 45° with<br />

point x <strong>and</strong> then over onto the horizontal C T line. The one<br />

that’s higher at low pH is protonate; the one that is higher at<br />

high pH is dissociated.<br />

f. Now draw the H + <strong>and</strong> OH - lines. These are 45° lines that cross<br />

at pH = 7<br />

4. Write the charge balance (electroneutrality) equation * . Find the<br />

location on your graph where it is satisfied. Usually only one<br />

negatively charged species <strong>and</strong> one positively charged species will be<br />

significant, <strong>and</strong> the others will be low enough to neglect.<br />

5. Once you have this point, it gives you the pH <strong>and</strong> the concentration<br />

(-log 10 concentrations) for all species.<br />

We will stop with this application. But this type of graph can be used to<br />

analyze titrations, precipitation, equilibria with the atmosphere or other gas<br />

phases, <strong>and</strong> mineral equilibria.<br />

* Any species with more than one + or – charge must include this coefficient<br />

in the equation. Remember, it is moles of charge not moles of compound<br />

that is being considered. For example, adding Ca(OH) 2 to H 2 O, we would<br />

write<br />

2 [Ca 2+ ] + [H + ] = [OH - ]


Appendix: How the pC-pH graph is obtained from the equilibrium<br />

equations (eqn. 3 <strong>and</strong> eqn. 4).<br />

1. First consider the low pH region, where pH K a . Equation 4 was<br />

- CTKa<br />

[ A ] =<br />

+<br />

Ka<br />

+ [ H ]<br />

The denominator can now be approximated by [H + ], so taking logs<br />

gives<br />

log 10 [A - ] = log 10 C T + log 10 K a – log [H + ]<br />

p[A - ] = pC T + log 10 K a + pH<br />

which is the 45° line upward * . Also using [H + ] >> K a , eqn. 3 gives<br />

p[HA] = pC T , the horizontal line.<br />

2. Now at high pH, we have [H + ]

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