

Section 1
Section 2
Section 3
Section 4
Section 5
Section 6
Section 7
Section 8
Section 9
Section 10
Appendices
Appendix A
Appendix B
Appendix C
Appendix D
Appendix E
Appendix F
Appendix G
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(Source: Illinois Urban Manual Technical Committee)
DEFINITION
The removal of water from construction sites.
PURPOSE
The purposes of this practice are as follows:
CONDITIONS WHERE PRACTICE APPLIES
The practice applies to any construction site (includes any onsite and offsite excavated areas), where the presence of water creates unsafe conditions, potential damage, or restricts construction operations.
Construction sites where water is present in any form, including intermittent runoff, streams, standing water, ground water, or other bodies of water.
CRITERIA
Dewatering shall consist of the removal of surface water and/or ground water by diverting and/or removing water from construction sites, within a watershed, as needed to perform the required construction in accordance with the specifications.
All outlets for dewatering discharges shall be stable and protected from erosion.
Diverting Surface Water – Cofferdams, channels, sumps, flumes, and temporary diversions shall be built and maintained, as needed.
Installation of cofferdams and sumps shall follow the requirements as outlined in practice standards COFFERDAM 803 (in development) and SUMP PIT 950.
Excess surface runoff shall be diverted from the construction area as outlined in the practice standards TEMPORARY DIVERSION 955, TEMPORARY SWALE 980, DIVERSION 815, and DIVERSION DIKE 820.
A permanent stream or other concentrated flow shall be diverted away from the construction area as outlined in practice standard TEMPORARY STREAM DIVERSION 976 (in development) .
Removing Water – Drains, sumps, pumps, casings, well points and all other items required to dewater the site shall be furnished, installed and maintained.
Well points and deep wells shall be placed in intervals along the construction area as necessary to depress the groundwater table during construction. Monitor wells shall be installed where measurement of the effectiveness of the pumping is required. Well point and deep well dewatering shall be terminated as soon as practical.
In poorly drained soil areas, or where well dewatering is not practical, pumping directly from the construction trenches shall be allowed.
Erosion and Sediment Control – All dewatering activities shall be done in a manner that does not negatively impact the water quality of the water table or cause erosion or transport sediment or other pollutants.
Sediment removal shall be provided using the following practices or combination of practices depending on the sediment, dewatering method, location, and amount of dewatering:
Where sumps are used, they shall meet the requirements of SUMP PIT 950. In addition, where space is available, TEMPORARY SEDIMENT TRAPS 960 shall be used to detain water and remove sediment from pumping and diversion operations. Where there is limited space a PORTABLE SEDIMENT TANK 895 shall be used to retain sediment from dewatering operations. POLYACRYLAMIDE (PAM) FOR TURBIDITY REDUCTION AND SEDIMENT CONTROL 894 (in development) may also be used, as appropriate.
Where there is low, intermittent amounts of dewatering, pumps with filtration bags shall be used. Filtration bags shall be attached to pump discharges and surrounded with a secondary containment or on a stabilized area. Filter bags shall not be placed, whole or partially, within aquatic areas (wetlands, streams, etc.)
The material for the filtration bag shall meet the requirements of material specification 592 GEOTEXTILE, Table 2, Class I with a minimum tensile strength of 200 lbs. The filtration bag shall be sized per manufacturer recommendations and based on the size of the pump. The largest size pump to be used with a filtration bag shall be 4-inch diameter.
Removal of Dewatering Facilities - The temporary dewatering areas shall be removed after they have served their purpose. The dewatering areas shall be graded and stabilized with appropriate erosion control practices. The dewatering sites after removal shall not create any obstruction of the flow of water or any other interference with the operation of or access to the permanent works.
CONSIDERATIONS
Federal, state, county and/or local water quality requirements also need to be considered when choosing a dewatering method and may include a requirement for sampling and evaluating discharges for clarity.
Base the location, method of dewatering, and configuration on site conditions. The following items should be considered when selecting the proper dewatering method:
Evaluate function, need, velocity control, outlet stability, and site aesthetics. The location and capacity of temporary diversion and protective works should be based on the characteristics of the site, accessibility, and the potential damage during development. Secondary containment should be considered when the damage that would occur is high if the dewatering method and sediment control measures were damaged or failed.
An analysis of the effects of dewatering a site should also be considered. For example, permanent dewatering of a site may cause subsidence of surface areas and cause settlement cracks in foundations, cracks in pavements and uneven settlement of structures. Also, temporary dewatering may create dry areas during construction but the effect of allowing water tables to rise after construction may result in excess pressure on basement walls causing cracks and excessive or constant sump pump cycling.
PLANS AND SPECIFICATIONS
Plans and specifications for installing and building dewatering devices shall be in keeping with this standard and shall describe the requirements for applying the practice to achieve its intended purpose. At a minimum include:
All plans shall include installation, inspection, and maintenance schedules with the responsible party identified.
Methods of dewatering shall be constructed to meet the requirements of construction specification 11 REMOVAL OF WATER.
OPERATION AND MAINTENANCE
The frequency of inspections shall depend on the dewatering method, amount of discharge, potential damage, and quality of the receiving bodies of water. The frequency of inspections and specific tasks shall be identified.
REFERENCES
Maine Department of Environmental Protection, Bureau of Land and Water Quality. Maine Erosion and Sediment Control BMPs. G-3 Construction Dewatering. Augusta, ME. March 2003.
June 2010
urbst813.doc