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Town of Southborough, MA
Worcester County
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Table of Contents
Table of Contents
The location and installation of each individual sewage disposal system or other means of disposal shall be such that, with responsible maintenance, it will function in a satisfactory manner and will not create a nuisance or discharge into any watercourse of the commonwealth. In determining a suitable location for the system, consideration shall be given to the size and the shape of the lot, slope, natural and adjusted drainage, existing and known future water supplies, depth to groundwater, presence of impervious material, soil classifications and reserve area. No disposal works construction permit, as described in § 223-2, shall be issued until a representative of the approving authority has:
A. 
Performed a site examination.
B. 
Witnessed deep observation holes.
C. 
Witnessed percolation tests.
D. 
Approved the proposed sewage disposal plan.
The site examination shall be made to determine if the size of the lot is compatible with the proposed sewage disposal system and should be made with regard to the distances outlined in § 223-32 and the requirements of § 223-6.
A. 
The purpose of the deep observation hole is to determine the character of the soil in the leaching area and specifically to determine the groundwater elevation and the presence of impervious material. On any lot, in the area to be used for leaching, except as noted below, there will be at least two observation holes, plus any additional number which, in the opinion of the approving authority, will be necessary to determine the consistency (or lack thereof) of the character of the soil. The observation holes shall be examined to a depth of at least four feet below the bottom of the proposed leaching facility but in no case shall be lower than 10 feet, unless this depth is unattainable because of bedrock, etc. The groundwater elevation should be determined when the groundwater is at its maximum elevation.
B. 
Exception. In cases where three or more contiguous single-family uses are being examined at the same time by the same engineer, the requirement of two deep observation holes per lot is reduced to one deep observation hole per lot, provided that the character of the soils remains consistent in the opinion of the approving authority. The deep observation holes shall be conducted in the area to be used for leaching on each lot.
The purpose of the percolation test is to determine the suitability of the soil at the leaching elevation and to a depth of four feet below this elevation. In cases where the soil varies with depth as indicated by the deep observation holes, percolation tests at various elevations may be required by the approving authority.
A. 
At least two percolation tests shall be performed at the site of each disposal area in the soil to be used for leaching. Additional tests will be required where the soil structure varies or where large disposal areas are required. Percolation tests can be performed at any time of the year.
B. 
Percolation tests, as prescribed in this section, shall be performed, at no expense to the approving authority, by a registered professional engineer. All percolation tests shall be performed in the presence of a representative of the approving authority. The cost of labor and equipment necessary to dig observation holes and the provision of water for the performance of percolation tests shall not be at the expense of the approving authority.
C. 
Percolation tests shall not be made in holes that have remained open to the atmosphere for more than three days, nor shall they be made in frozen soil. Percolation tests may be performed when the elevation of the soil to be tested is below the frozen soil layer.
D. 
Percolation tests shall not be made in filled ground unless the requirements of § 223-20 have been made.
E. 
The minimum leaching area to be installed shall be determined from the following table, with the estimated sewage flow as determined in accordance with § 223-16. The slowest percolation rate obtained shall govern leaching area requirements.
Leaching Area Requirements1, 4, 6, 7, 8
Sidewall Area2, 9
Percolation Rate
(minutes per inch)
Square Feet Per Gallon
Gallons Per Square Foot
Bottom Area3
0.0 to 10.0
1.0
1.00
15.0
1.5
0.67
20.0
2.0
0.50
25.0
2.5
0.40
30.0
3.0
0.33
Over 30.05
Unsuitable
NOTES:
1 Leaching fields: see Article XV.
2 Sidewall area is the pervious vertical interface of the excavation for the leaching facility below the invert elevation of the inlet, or the lowest invert elevation of the distribution line.
3 Bottom area will not be considered as part of the leaching facility without prior approval of the Board of Health.
4 Systems for more than 2,000 gallons per day shall not be installed where the percolation rate is slower than 20 minutes per inch.
5 Soil with a percolation rate over 30 minutes per inch is considered impervious and, therefore, unsuitable for the subsurface disposal of sewage.
6 Garbage grinders are not allowed.
7 Sewage systems to be constructed in fill must be designed according to the percolation rate of the underlying original soil.
8 See Illustrations A and B (on file in the Town offices).
9 Minimum allowable square footage by the Southborough Board of Health is 450 square feet of sidewall area only.
A. 
Prepare test hole into the proposed leaching strate, within the disposal area, of 12 inches in diameter with vertical sides, 18 inches deep.
B. 
Establish a fixed point at the top of the test hole from which all measurements can be taken.
C. 
Scratch the bottom and sides of the test hole to remove any smeared soil surfaces. Either add two inches of coarse sand to protect the bottom from scouring or insert a board or other impervious object in the hole so that water may be poured down or on it during the filling operation.
D. 
Carefully fill the hole with clear water to a minimum depth of 12 inches and maintain the water level by adding water as necessary for the purpose of soil saturation, but in no case less than 15 minutes after first filling the hole.
E. 
After saturation, if the water level drops to a depth of nine inches in less than 30 minutes, measure the length of time in minutes for it to drop from a depth of nine inches to a depth of six inches. If the rate is erratic in the opinion of the approving authority, the hole shall be refilled and soaked until the drop per increment of time is steady. The time for the level to drop from a depth of nine inches to a depth of six inches divided by three will be the percolation rate in minutes per inch.
F. 
If the initial three-inch drop requires more than 30 minutes (rate equal to more than 10 minutes per inch), the soil shall be saturated by filling the hole to the top and maintaining it full for at least four hours. The soil shall then be permitted to swell overnight so that the soil conditions will approach those which exist during the wettest season of the year. After the overnight swelling period, the test shall be made again by filling the hole to a twelve-inch depth and maintaining that level for 15 minutes, letting the level drop to nine inches, then timing the drop between nine inches and six inches. The time elapsed between nine inches and six inches, divided by three shall be the percolation rate.
G. 
In certain soils, particularly coarse sand, the soil is so pervious as to make the percolation test as described above difficult, impractical and meaningless. Therefore, at the discretion of the approving authority, the test, as described above, may be waived, and a rate of two minutes per inch can be assumed, provided that at least 24 gallons of water is added to the percolation hole within 15 minutes and it is impossible to obtain a liquid depth of nine inches or the percolation rate is faster than 30 seconds per inch.
Subsurface sewage disposal systems shall be located in an area where there is at least a four-foot depth of naturally occurring pervious soil below the entire area of the leaching facility. The naturally occurring pervious soil shall have a percolation rate less than or equal to 30 minutes per inch, or 20 minutes per inch for systems over 2,000 gallons per day, and the four-foot stratum must be free of impervious material, such as layers of clay, silt, subsoil or loam.
No disposal facility shall be closer than the distances stated to the components listed in the following table. The distance shall be increased where required by conditions peculiar to a location.
Distances1, 2
Component
Septic Tank
(feet)
Leaching Facility
(feet)
Building Sewer
(feet)
Privy
(feet)
Well or suction line
50
1001
3
1001
Water supply line (pressure)
4
4
4
4
Property line
10
10
30
Cellar wall or in-ground swimming pool
10
20
30
Surface water supplies (reservoirs or tributaries to reservoirs), including open and subsurface drains
502, 5
1001, 2, 5
5
1001, 2, 5
Watercourses
252, 5
502, 5
502, 5
Subsurface drains
25
25
25
Leaching catch basin or dry well
25
Downhill slope (measured from the top of the leaching facility)
150 times the slope (expressed as a fraction) (See Illustrations A, B, C, on file in Town offices.)
NOTES:
1 One hundred feet is a minimum acceptable distance, and no variance shall be grated for a lesser distance, except with prior written approval of the Department of Environmental Quality Engineering.
2 All distances shall be measured from the average of the mean annual flood elevation in inland areas and from mean high water in coastal areas.
3 Ten feet if constructed of durable corrosion-resistant material with water tight joints or 50 feet if any other type of pipe is used.
4 It is suggested that the disposal facilities be installed at least 10 feet from the 18 inches below water supply lines. Wherever sewer lines must cross water supply lines, both pipes shall be constructed of Class 150 pressure pipe and should be pressure tested to assure watertightness.
5 The applicant should be aware of his obligation to comply with the requirements of the Wetlands Protection Act. MGL c. 131, § 40.