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presence of NH 4 Cl (129.65 mg/l) than in the presence of NH 4 NO 3 (109.25 mg/l) as
reported by Habte and Osorio ( 2012 ). The concentration of P solubilized by
Mortierella sp. in the presence of KNO 3 was only 0.08 mg/l. Moreover, the excess
of NH 4 + adversely affected the growth of Mortierella sp. In the presence of NO 3
as the only source of N, Mortierella sp. not only dissolves a small amount of
inorganic phosphate (Pi) from the RP but also immobilizes most of it into its
mycelia. In contrast, in the presence of NH 4 Cl, Mortierella sp. has been effective
in dissolving RP, and the Pi released remained in solution, while only a little portion
was immobilized by the fungal mycelia (Habte and Osorio 2012 ). In yet another
investigation, ammonium significantly decreased mineral phosphate solubilization
(mps) in a wild-type Mps + strain IR94-MF1 and superpositive Mps ++ of Penicillium
rugulosum mutants (Reyes et al. 1999 ). Also, ammonium in most of the studies has
been found as a better N source than nitrate (Wenzel et al. 1994 ; Asea et al. 1988 ),
and P. fluorescence, for example, utilized (NH 4 ) 2 SO 4 most efficiently and signif-
icantly decreased the pH of the medium during P solubilization. According to
Sulbaran et al. ( 2009 ), P. agglomerans MMB051, when grown in the presence of
KNO 3 , as an alternative N source, instead of (NH 4 ) 2 SO 4 , changed the final pH of
the culture supernatant which was almost two units higher (pH 5.1
0.15) than that
recorded for (NH 4 ) 2 SO 4 (pH 2.86
0.21). The final concentration of soluble P by
P. agglomerans MMB051 was however lower in supernatant prepared from cells
grown in medium treated with KNO 3 (58.15 mg/l) relative to those recovered from
(NH 4 ) 2 SO 4 -grown cells (95.75 mg/l). In bacteria, although different NO 3 trans-
porter systems have been identified, nitrate/proton symporter is the main transporter
for NO 3 (Rowe et al. 1994 ; Kucera and Kaplan 1996 ). Consequently, there may be
an increase in extracellular pH due to NO 3 uptake by bacterial cells (Crawford and
Glass 1998 ) which possibly could explain the differences in the P-solubilizing
abilities of P. agglomerans MMB051 cells grown in the presence of NH 4 + or
NO 3 ions (Sulbaran et al. 2009 ). Similar effect of different N sources on PS
activity has been reported (Roos and Luckener 1994 ; Relwani et al. 2008 ).
3.2.5 Effect of CaCO 3 and Aeration
Acidic soils are generally limed to adjust the pH of the soil, while pyrite and
gypsum are used to amend alkaline/saline soils. However, addition of CaCO 3 to
the medium markedly reduces P solubilization by bacteria and fungi in liquid
media. For example, Enterobacter intermedium , isolated from grass rhizosphere,
even though had a strong ability to solubilize insoluble P, the concentration of
soluble P was significantly decreased to 200-250 mg/l when grown in medium
treated with 1 % CaCO 3 compared to medium without CaCO 3 (1,000 mg/l).
Furthermore, the bacteria oxidize glucose to gluconic acid and sequentially to
2-keto-gluconic acid (2-KGA) (Hwangbo et al. 2003 ). Similarly, calcium added
as CaCl 2 ,CaCO 3 , and Ca(OH) 2 to the medium reduces the P solubilization by
Rhizobium and Bradyrhizobium from RP because CaCO 3 enhances the pH of the
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