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               exposed  to  100  mg/L  Al(OH) 3  for  59  days.  The  excessive  amounts  of  calcium  lead  to
               precipitation of carbonate and phosphate, which affect biomass activity because of mass transfer
                                                                                2+
               limitations. A study from Yu et al. (2001) showed that the low Ca  concentration from 100-300
               mg/L  to  be  beneficial  for  sludge  granulation  in  an  UASB  reactor.  The  optimal  sodium
               concentration  for  mesophilic  aceticlastic  and  hydrogenotrophic  methanogens  growth  was  230
                                      +
               mg/L  and  350  mg  N /L,  respectively  (Kugelman  and  Chin,  1971;  Patel  and  Roth,  1977).
               Moreover, a study the effect of potassium and magnesium on microorganism’s growth  shows
                                                                 +
               that at high concentration of potassium (0.15 M K ) caused 50% inhibition of acetate-utilizing
               methanogens, while under high magnesium ions concentration, stimulate the production of single
               cell, which causes loss aceticlastic activity in the digesters. Consequently, under high salt levels
               could cause bacterial cells to dehydrate due to osmotic pressure, and therefore suppress microbial
               growth, and consequently affect specific growth rate.

                       Several  industrials  and  domestic  wastewater  was  found  a  significant  concentration  of
               heavy metals such as zinc (Zn), copper (Cu), cadmium (Cd), nickel (Ni), iron (Fe), chromium
               (Cr),  and  etc.  Heavy  metals  are  bio-available  and  it’s  a  necessary  as  nutrients  at  low
               concentration to microbial growth. Heavy metals are toxic when present in ionic form since it’s
               attributed to disruption of enzyme function and structure by binding to ion-exchange site on the
               cell  membrane  and  form  a  matrix  with  extracellular  enzymes.  Takashima  and  Speece  (1989)
               reported the following order of heavy metal composition in the cell of ten methanogenic strains:
               Fe >> Zn > Ni > Co = Mo > Cu, and also acidogens are more resistant to heavy metal toxicity
               than  methanogens.  There  are  several  forms  of  heavy  metal  such  as  precipitation  as  sulfide,
               carbonate, and hydroxides, and sorption to the solid fraction. There are, however, only metals in
               soluble, free form are toxic to the microorganisms (Oleszkiewicz and Sharma, 1990). The study
               from Lin (1993) showed that the relative toxicity of heavy metals in inhibition test on sensitivity
               of methanogens as Pb > Ni > Cd > Cu > Cr > Zn, while the relative toxicity of heavy metals on
               sensitivity of acidogens is Cu > Zn > Cr > Cd > Ni > Pb (Lin, 1992).
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