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8/9/2019 PKa Concepts
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pKa concepts
Ionization = the process in which ions are formedfrom neutral compounds;
Dissociation = the separation of the ions of anelectrovalent compound as a result of the actionof a solvent (usually water)
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For a weak acid, which dissociates as follows
!" # !$ $ "%
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"n interestin& and e'tremely useful relationship etween
p! and pKa can e otained simply y takin& lo&arithms
(to the ase *) of the previous e+uation
lo&*
Ka = lo&
*!$- $ lo&
*"% - % lo&
*!"-
.herefore
%lo&*!$- = %lo&*Ka $ lo&*"%- % lo&*!"-
/ote lo& a 0 lo& = lo& (a1)
&ivin& the !enderson%!asselalch e+uation
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.he most convenient form of this !enderson%!asselalche+uation, is
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2sin& pKa and p! relationship
3 4y usin& pKa values, we are ale to e'press thestren&th of an acid (i5e5 its tendency to dissociate)with reference to the p! scale5
3 If Ka is lar&e, then pKa will have a low numerical
value5 65&5,!ydrochloric acid, !7l has a pKa = %8
"cetic acid, 7!8799! has a pKa = :5
3 " stron& acid is one which is lar&ely, orcompletely, dissociated, and which therefore hasa high Ka value (and low pKa)5
3 " weak acid is one that is only sli&htly dissociatedin solution, and has a low Ka value5
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if we consider the situation where the acid
is one%half (<*) dissociated,
or where
"%- = !"-
(that is <* ne&atively char&ed and <* unchar&ed)
then, sustitutin& in the
!enderson%!asselalch 6+uation
p! = pKa $ lo&("%1!")
p! = pKa $ lo&()
.herefore p! = pKa $ *
and p! = pKa
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!ow to use !%! e+uation
3 >hen p! = pKa, the char&ed and unchar&edspecies have ?e+ual concentrations5
3 >hen p! @ pKa, the ionized (char&ed) form is
dominant, so there will e more ne&ative sites,
therefore, as pH increases, CEC increases
3 >hen p! A pKa, the un%ionized, unchar&ed form
is dominant, so there will e fewer ne&ative
sites, thus, as pH decreases, CEC decreases (and "67
increases)
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>hy care aout pKa in soilsB
3 767 increases as p! increases
6arly studies showed soil 767 was constant from
p! C5< 0 <
"t p! @ < the 767 of soil increased, especially in
soils containin& or&anic matter or non C clays
3 9r&anic and inor&anic components of soil
have functional &roups that dissociate atvarious p!s, leavin& them with a ne&ative
char&e that can attract cations
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"cidity of various soil functional &roups
3 Eome inor&anic surface functional &roups aremore likely to deprotonate or dissociate thanotherspKa of "l(9!C)$ = ?<, ("l%9!%Ei)$*5< = ?, Ei9! = ?5<
C silicate minerals have more Ei%9! &roups andcontriute less to p!%dependent char&e than minerals and metal o'ides
3 E9G contriutes the most ne&ative char&eH<%* of char&e due to deprotonation of 799! and
phenolic 9! &roups which have pKas of : 0 and %
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http11www5iolo&ie5uni%hamur&5de1%online1&e1*5&if
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7olloid/e&ative
char&e
Jositive
char&e constant variale
!umus C** * * *
ermiculite C* * < <
Emectite ** * < <
Illite :* * H* C*
Kaolinite C : < <
Fe L "l9'ides
< < * **