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The MBR Book: Principles and Applications of Membrane

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exploitation index (WEI), the values <strong>of</strong> which represent the annual mean total dem<strong>and</strong><br />

for freshwater divided by the long-term average freshwater resource. It provides an<br />

indication <strong>of</strong> how the total water dem<strong>and</strong> puts pressure on the water resource.<br />

Data from the year 2000 indicate that four European countries (Cyprus, Italy,<br />

Malta <strong>and</strong> Spain) representing 18% <strong>of</strong> Europe’s population, were considered to be<br />

water stressed. It is estimated that, in 1990, around 1.9 billion people lived in countries<br />

which used more than 20% <strong>of</strong> their potential water resources. By 2025, the<br />

total population living in such water-stressed countries is expected to increase to 5.1<br />

billion, this figure rising further to 6.5 billion by 2085. On the other h<strong>and</strong>, climaterelated<br />

water stress is expected to reduce in some countries, for example, the USA<br />

<strong>and</strong> China, while in central America, the Middle East, southern Africa, North Africa,<br />

large areas <strong>of</strong> Europe <strong>and</strong> the Indian subcontinent, climate change is expected to<br />

adversely increase water stress by the 2020s. It is also predicted that 2.4 billion people<br />

will live in areas <strong>of</strong> extreme water stress (defined as using more than 40% <strong>of</strong> their<br />

available water resources) by 2025, 3.1 billion by 2050 <strong>and</strong> 3.6 billion by 2085; this<br />

is compared with a total population <strong>of</strong> 454 million in 1990 (Met Office, 2006).<br />

1.4.5 Greater confidence in <strong>MBR</strong> technology<br />

A growing confidence in <strong>MBR</strong> technology is demonstrated by the exponential<br />

increase in the cumulative <strong>MBR</strong> installed capacity (Fig. 1.7). As existing wastewater<br />

treatment plants become due for retr<strong>of</strong>it <strong>and</strong> upgrade – normally relating to a<br />

requirement for increased capacity <strong>and</strong>/or improved effluent water quality without<br />

incurring a larger footprint – it is expected that opportunities for the application <strong>of</strong><br />

<strong>MBR</strong> technologies will increase, particularly in the USA. It is also evident that <strong>MBR</strong><br />

installations are increasing in size year on year; the largest installation is currently<br />

50 megalitres/day (MLD) with larger installations being planned <strong>and</strong> some observers<br />

stating that plants <strong>of</strong> 300–800 MLD are feasible (DiGiano et al., 2004).<br />

With new factors coming into play, the <strong>MBR</strong> technology is now beginning to<br />

mature such that the market is expected to grow substantially over the next decade.<br />

Evidence suggests that <strong>MBR</strong>s will continue to penetrate further the effluent treatment<br />

market, with the number <strong>of</strong> players in the global market increasing. Currently,<br />

the market is dominated by the two leading companies Zenon <strong>and</strong> Kubota. Whilst<br />

the domination <strong>of</strong> these two companies is likely to continue in the short to medium<br />

term, the global dem<strong>and</strong> for the technology is such that a broader range <strong>of</strong> products is<br />

likely to be sustainable in the future (Chapter 4), in particular if individual products<br />

are tailored towards niche market applications.<br />

1.5 Historical perspective<br />

1.5.1 <strong>The</strong> early days <strong>of</strong> the <strong>MBR</strong>: the roots <strong>of</strong> the Kubota <strong>and</strong> Zenon systems<br />

Introduction 11<br />

<strong>The</strong> first membrane bioreactors were developed commercially by Dorr-Oliver in the<br />

late 1960s (Bemberis et al., 1971), with application to ship-board sewage treatment

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