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12<br />

relation to water and chemical consumption, water consumption pattern, necessary water<br />

quality and wastewater characterization, economic conditions as well as the general situation<br />

of the enterprises. Based on the answers and on interviews of the enterprises 7 potential<br />

primary plants and 6 potential secondary plants were selected to participate in the project.<br />

The identification of the grey water resources of the potential primary plants indicated that<br />

institutions such as swimming baths, public schools and sports centres can contribute considerable<br />

grey water resources as it is seen from Table 0.1.<br />

Table 0.1 Survey of potential primary plants and their grey water resources in the municipality<br />

of Herlev.<br />

Primary plants Grey water resources<br />

[m 3 /year]<br />

Type of water<br />

Swimming baths<br />

3.200 – 5.500<br />

1.200 – 2.100<br />

Shower water<br />

Filter rinse water<br />

Public schools 1.000 Shower water<br />

Sports centres (Icerink) 1.200 Cleaned ice*<br />

Hospital 22.000 Rain water**<br />

Industrial production enterprises<br />

4.400<br />

RO-concentrate (dilute),<br />

distillation water<br />

750 Conc. cleaning water<br />

* Seasonal grey water resource (1/9 – 1/4).<br />

** Rain water was included as a potential grey water resource due to a large existing water collection<br />

facility.<br />

A spot check analysis of the grey water from 4 potential primary plants was performed for<br />

determination of pertinent physical-chemical and microbiological parameters.<br />

Grey water from swimming baths and other institutions, where the principal source of the<br />

grey water production comes from showering, is estimated to contain a certain potential for<br />

microbiological after-growth in situations where the grey water is to be collected and stored<br />

in equalizing tanks (COD: 50 – 100 mg/l, SS: 100 – 200 mg/l, total – N: 5 – 10 mg/l, total –<br />

P: 1 – 2 mg/l). Due to technical problems it was only possible to analyse the filter rinse<br />

water from swimming baths and the quality of shower water from institutions having typically<br />

a large consumption of water for showering was consequently estimated based on<br />

other studies of similar types of grey water.<br />

At industrial manufacturing enterprises slightly polluted wastewater from production-like<br />

conditions was classified as grey water. However, the quality of the grey water varies much<br />

dependent on which type of process the water comes from. For example, the quality of grey<br />

water from a medical production enterprise was found to almost meet the requirements of<br />

the Executive Order on Drinking Water (Danish Ministry of Environment). Another enterprise<br />

manufacturing cleaning materials produced less amounts of grey water during their<br />

cleaning of the process tanks, but in this case a considerable degree of pollution was seen in<br />

relation to COD (> 3.000 mg COD/l).<br />

Rainwater – collected at the Herlev County Hospital – was also included in the study because<br />

of an important surplus production. This type of water was estimated to be periodically<br />

very unhygienic because of a heavy after-growth of microbes in certain periods. Due<br />

to a low hardness, conductivity and salinity, however, the technical water quality was estimated<br />

to be high apart from the winter periods, where salt is sprinkled.

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