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Practical example of information to be considered.
Route |
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Personnel |
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Scheduling based on vacation, sick leave, experience, practical knowledge, training
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Medical condition
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Additional personnel from other crews
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Vehicles |
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Equipment |
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Hose length
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Nozzle type
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…
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The information required by EN 14654 should be included in the inventory and attribute data. If this is not the case, the missing information should be determined by a site visit. If the appropriate cleaning method has been determined, their application will be optimised. (Image: Optimization operating parameters)
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The target of a resource-saving use of personnel and vehicles has to be organised via an operational and flushing plan. This is achieved for example by: -
A reduction of travelling times between the individual sections to be cleaned
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A continuous section by section cleaning up to the next larger collector to minimise the risk of deposits below the cleaned section
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Taking account of other factors resulting from the network and development structures…
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For an optimisation of the operational or flushing plans the following operational data should be considered: (Table: Operational data of high-pressure cleaning)
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The relationship of the section-dependent and section-independent costs must also be considered in the optimisation process (Table). (Table: Section-dependent and -independent costs incurred in high-pressure cleaning)
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Time distribution of high-pressure cleaning (Image: Limits of variations of required time for operations during sewer cleaning (8-h-day)) (Image: Time required for operations during sewer cleaning (8-h-day) in percent)
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Below you can see extracts from an example flushing plan. The following details can be gathered from the database:
catchment
area |
plan |
starting manhole |
target manhole |
street |
length |
type of drainage system |
material code |
cross-section code |
height |
width |
year of const. |
realised rehabilitation |
in [year] |
3 |
478 |
8904004049 |
8904004050 |
Weststr |
50,36 |
combined |
20 |
10 |
400 |
400 |
1925 |
partliner |
1999 |
3 |
478 |
8904004050 |
8904004051 |
Weststr |
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(Image: Arrow Step 03) In step 3, the cleaning planning is implemented based on the developed operational and flushing plans.
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During cleaning, the collected waste is to be checked as regularly as possible. A higher proportion of mineral solids and broken pipe bits indicates serious damage, e.g. pipe fracture or collapse. In such situations, the cleaning procedures have to be stopped immediately and protective measures have to be taken. If required, a less destructive cleaning method is to be chosen before cleaning is continued. (Image: Look at the waste material)
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Disposal of the collected waste material.
(Image: Stockpiling of the solid waste material at the service depot) |
(Image: Disposal of the liquid waste material directly into the sewage treatment plants feeder line) |
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Since June 1, 2005, the dumping of biodegradable waste - including the waste material from sewer cleaning procedures - without a prior thermal or appropriate mechanical-biological treatment is only permitted, insofar as the organic portion of the dry residue (measured as loss due to heating) does not exceed the values given: -
3 % by weight: Geological barrier, Landfill class 0 and I
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5 % by weight: Landfill class II
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10 % by weight: Landfill class …
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According to [Billm2002], a maximum of 40 – 50 % of the waste material from sewers, and a maximum of 15 – 25 % of the waste material from catch basins can be classified as recyclable substances. The re-utilisation potential of the waste material from the cleaning of sewers is limited to a fraction of the mineral solids. (Image: Disposal of waste material) (Image: Dewatered waste material in the holding tank of the cleaning vehicle)
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The same applies to the waste material from catch basins. There is an additional re-utilisation potential for the ferrous and non-ferrous metals bound to particles [Billm2002]. (Image: Re-utilisation potential of the waste material from catch basins) (Image: Waste in catch basin) (Image: Disposal of waste)
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Currently, the waste material from sewers and catch basins is, in most cases, dumped or thermally treated. Mineral solids are only recycled in exceptional circumstances and then re-utilised in the following fields:
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(Image: Cleaning – Disposal of waste material)
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(Image: Arrow Step 04) After the cleaning measures are completed, quality control is carried out in step 4. -
The cleaning performance and results are documented. This ensures that inadequately or insufficiently performed cleaning measures are immediately detected, and the service provider can be asked to undertake improvements
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Furthermore, the documented quality control information ensures a constant update to the much needed operational knowledge …
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(Image: Picto Fakten) According to EN 14654-1, the manner of inspection and approval of the cleaning measures should be specified and available before the start of the cleaning measures. This specification should include the following: -
A description of the required cleaning results
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General requirements regarding the documentation inclusive of a description of the achieved cleaning results and the circumstances under which these results were obtained
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Important: Performance indicators are to be chosen in such a way that they can clearly show whether the required performance was achieved. Especially suitable are easily quantifiable parameters, such as: (Image: Permissible level of deposits) (Image: Mass of deposits) (Image: Volume of deposits)
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(Image: Quality control – Diagram)
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(Image: Picto Liste) The acceptance protocol should contain: -
Place, date and time of the performed services
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Name of contractor, name of on-site inspector
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Assessment of the sewer line condition before cleaning
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The cleaning method and equipment used
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Type and amount of removed waste material. Estimation of the structural and hydraulic state of the sewer line after cleaning
(Table: Example for an acceptance protocol of a sewer cleaning modelled after […
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(Image: Picto Liste) It is appropriate to amend the protocol by further fields to be able to document additional relevant operational data. These can for example include: -
The accessibility of the manholes
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Special characteristics (noise, development of odours)
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Cleaning objective and parameters
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Number of flushing cycles
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Time consumed for cleaning
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Water consumption
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Quantity or volume of waste material
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Time consumed for water refilling
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…
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(Image: Picto Liste) -
Time consumed to change over the cleaning vehicle
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Time consumed to dump the waste material
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Other efforts and expenses, etc.
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Inspection technology used to determine the cleaning result
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Deviations from the operational/flushing plan
This information is the basis for the update and constant optimisation of the demand- and state-oriented cleaning planning.
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The assessment methods which are used to confirm the correlation between the specified (tender) and actual services should include: -
Optical inspection of the manhole and access shafts
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Optical inspection of the sewer line, via mirroring, video inspection via cart or drone
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Where appropriate, sewer measuring boat, culvert pressure unit, sonar measurement
The contract specifications should outline whether these tests are to be carried out at random…
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(Image: Frage) The following questions should already be considered with regard to quality control and documentation: -
Has the drainage capacity of the sewer been re-established?
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Have complaints due to odour nuisance decreased to the specified extent?
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Has the planned residual sedimentation height in the cleaned sections been undercut?
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Was a maximum deposit height achieved as a percentage of the sewer profile height?
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