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Percolation Test Method

A preliminary assessment should be carried out including consultation with the Environment Agency and local authority to determine the suitability of the site, the natural vegetation on the site should also give an indication of its suitability for a drainage field.

A trial hole should be dug to determine the position of the standing ground water table and the trial hole should be a minimum of 1m2 in area and 2m deep, or a minimum of 1.5m below the invert of the proposed drainage field pipework.

The ground water table should not rise to within 1mtr of the invert level of the proposed effluent distribution pipes. If the test is carried out in summer the likely winter groundwater levels should be considered.

A percolation test should then be carried out to assess the further suitability of proposed area.

A hole 300 mm square should be excavated to a depth 300 mm below the proposed invert level of the effluent distribution pipe., where deep drains are necessary the hole should conform to this shape at the bottom, but may be enlarged above the 300 mm level to enable safe excavation to be carried out.

Where deep excavations are necessary a modified test procedure may be adopted using a 300 mm earth auger, bore the test hole vertically to the appropriate depth taking care to remove all loose debris. Fill the 300 mm square section of the hole to a depth of at least 300 mm with water and allow it to seep away overnight.

Next day refill the test section with water to a depth of at least 300 mm and observe the time in seconds for the water to seep away from 75% full to 25% full level (i.e. a depth of 150mm). Divide this time by 150mm and the answer gives the average time in seconds (Vp) required for the water to drop 1 mm.

The test should be carried out at least three times with at least two trial holes, the average figure from the tests should then be taken.

The test should not be carried out during abnormal weather conditions such as heavy rain, severe frost or drought.

Drainage field disposal should only be used when percolation tests indicate average values of Vp of between 12 and 100 and the preliminary site assessment report and trial hole tests have been favourable. This minimum value ensures that untreated effluent cannot percolate too rapidly into ground water.


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Essex 
Chelmsford, Basildon, Romford, Southend, Colchester, Harlow, Brentwood, West Ham, Ashdon CB10, Basildon SS14, Billericay CM11,Blackmore CM4, Boxted CO4, Braintree CM7, Brightlingsea  CO7, Buckhurst Hill IG9, Burnham-on-Crouch CM0, Canewdon SS4, Canvey Island SS8, Chelmsford CM1, Chrishall SG8, Clacton-on-Sea CO15, Clavering CB11, Coggeshall  CO6, Colchester CO1, Coxtie Green CM14, Danbury CM3, Earls Colne CO6, Epping CM16, Frinton-on-Sea CO13, Fyfield CM5, Good Easter CM1, Great Bentley CO7, Great Dunmow CM6, Great Easton CM6, Great Leighs CM3, Great Sampford CB10, Great Yeldham CO9, Hadleigh SS7, Halstead CO9, Harlow CM17, Harwich CO12, Hatfield Heath CM22, Havering RM12, Hockley SS5,Hornchurch RM12, Ingatestone CM4, Jaywick CO15, Kelvedon CO5, Layer de la Haye CO2, Leigh-on-Sea SS9, Maldon CM9, Manningtree CO11, Matching CM17, Moreton CM5, Nazeing EN9, North Weald CM16, Peldon CO5, Pleshey CM3, Purfleet RM19, Purleigh CM3, Radwinter CB10,Ramsey CO12, Rayleigh SS6, Rickling CB11, Ridgewell CO9, Rowhedge CO5, Roxwell CM1, Roydon CM19, Saffron Walden CB10, Sheering CM22, Shoeburyness SS3, Silver End CM8, South Benfleet SS7, South Ockendon    RM15, Southend-on-Sea SS1, St Osyth CO16, Stanford-le-Hope SS17, Stansted Mountfitchet CM24, Stebbing CM6, Steeple Bumpstead CB9, Stock CM4, Terling CM3, Thaxted CM6, Theydon Bois CM16, Tilbury RM18, Tillingham CM0, Tiptree CO5, Tolleshunt D'Arcy CM9, Twinstead    CO10, Weeley CO16, West Mersea CO5, White Roding CM6, Wickford SS12, Willingale CM5, Witham CM8, Wivenhoe CO7