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The MBR Book: Principles and Applications of Membrane

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152 <strong>The</strong> <strong>MBR</strong> <strong>Book</strong><br />

No trend is evident in this data subset, though all but the highest (<strong>and</strong> probably<br />

non-optimal) SAD p values lie within the range 20–40.<br />

(b) HF systems tend to operate at lower permeabilities (generally �200 LMH/bar)<br />

<strong>and</strong> are associated with lower aeration dem<strong>and</strong>s, sometimes achieved by employing<br />

aeration intermittently. For these systems the permeability attained is roughly<br />

linearly related to aeration dem<strong>and</strong> (Fig. 3.2), with around 0.4 m 3 permeate generated<br />

per Nm 3 air per bar, <strong>and</strong> SAD p values are generally between 15 <strong>and</strong> 30.<br />

Conventionally <strong>MBR</strong>s, in common with all membrane processes, are designed on<br />

the basis <strong>of</strong> operating flux. However, permeability more accurately reflects the fouling<br />

condition <strong>of</strong> the membrane. Although the permeability <strong>of</strong> the virgin membrane<br />

material varies somewhat from one membrane product to another, a low operating<br />

permeability is generally indicative <strong>of</strong> a high degree <strong>of</strong> fouling. Given that permeability<br />

is the ratio <strong>of</strong> flux to TMP, then operation within given boundaries <strong>of</strong> permeability<br />

will necessarily determine the range <strong>of</strong> operational TMP values <strong>and</strong> vice versa.<br />

According to Fig. 3.3 it follows that, for HF systems at least, the required aeration<br />

rate for maintaining a given permeability (or TMP for a given target flux) can be estimated<br />

from the permeability itself. Alternatively, flux can be correlated with aeration<br />

rate from data depicted in Fig. 3.4; that is:<br />

SAD � 0.0044J �0.708<br />

for FS module<br />

m net<br />

SAD � 0.0052J �0.326<br />

for HF module<br />

p net<br />

although clearly more data is required to ratify such correlations.<br />

(3.18)<br />

(3.19)<br />

3.3.1.2 Cleaning<br />

A summary <strong>of</strong> physical <strong>and</strong> chemical cleaning protocols for the pilot plant study<br />

data (Table 3.22) <strong>and</strong> full-scale installation data (Table 3.23) reveals that physical<br />

cleaning is predominantly by relaxation rather than backflushing. Pilot plant data<br />

indicate downtime for physical cleaning to account for between 4% <strong>and</strong> 20% <strong>of</strong> the<br />

operating time, with no pr<strong>of</strong>ound difference between the two configurations. On the<br />

other h<strong>and</strong>, maintenance cleaning every 3–14 days is routinely employed for some<br />

HF technologies whereas chemical cleaning is usually limited to recovery cleans<br />

alone for FS systems.<br />

For both FS <strong>and</strong> HF systems recovery cleans are generally applied at intervals <strong>of</strong><br />

6–18 months depending on flux. Recovery cleans generally employ hypochlorite<br />

concentrations between 0.2 <strong>and</strong> 1 wt% NaOCl (Table 3.9), usually adjusted to a pH<br />

<strong>of</strong> �12. Both maintenance <strong>and</strong> recovery cleaning are brief <strong>and</strong>/or infrequent enough<br />

to add little to the percentage downtime. For example recovery cleans at Porlock <strong>and</strong><br />

Brescia have been applied, on average, once every 9 <strong>and</strong> 15 months respectively. Even<br />

for an overnight soak <strong>of</strong> 16 h, the total downtime for cleaning amounts to �0.25%<br />

in such cases. For Zenon sewage treatment plants the maintenance cleaning cycle<br />

normally incurs no more than 2 h <strong>of</strong> downtime <strong>and</strong> is employed once every one or

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