HomeMy WebLinkAbout1987-05-05 Septic System Design ReportJ
AV,40 r;� �*r
7 Hakanson
Anderson
Assoc., Inc.
May 5, 1987
Mr. Jim Johnson
8327 W. Bush Lake Road
Bloomington, FIN 55438
Dear Jim:
Jame_;! :. yoknson
Aelen L. Jofwon
8.127 11Pat Bus/t Lake Road
�Bloontingtott, ;11�( 554.38
Engineers, Surveyors &
Landscape Architects
At your request, a site evaluation to determine soil suitability
for on -site sewage treatment was performed at Lot 4, Block 1, Bill
Kelley's Land in the City of Orono, Minnesota. Standard methods of
percolation testing were employed. Elevations are relative to an
assumed elevation of 100.0 based at the top of a single spike in a
six inch diameter elm tree east of the test site (see enclosed
sketch).
This report includes:
1. Soil boring logs
2. Percolation test results
3. Testhole location and septic system configuration.
sketch
4. Septic system design specifications
5. Discussion and recommendations.
The soil boring logs show that sandy loam to sandy clay loam sur-
face soils overlie sandy clay loam to sandy clay subsurface soil
horizons. Soil mottling begins at 1.5 to 2.5 Z."at depth at the
boreholes. Soil mottles (spots of contrasting color) are accepted
indicators of periodic saturation in soils. Soil gleying begins at
2.0 to 3.0 feet depth at the boreholes. Gleying (dull gray soil
color) fortes in soils which are saturated and in a chemically
reduced condition for long periods of time. Ground water was
encountered at elevation 91.8 at borehole #4 on April 24, 1987.
Percolation test results are as follows:
Soil Texture at
Hole Elevation Depth (inches) Bottom of Hole
P-1 99.5 16 Sandy loam
P-2 99.9 12 Sandy loam
Percolation Rate
(min/in)
1
6
222 Monroe Street
Anoka, Minnesota 553C
612/427-SW
Eugene J. Hakanson, CE
James M. Winter. LS.
Lawrence 4 Koshak. PL
Peter R. Raatikka, P.E
Mr. Jim Johnson
May 5, 1987
Page Two
P-3 100.9
30 Sandy
clay
loam 6
P-4 100.9
24 Sandy
clay
loam 7
P-5 98.0
24 Sandy
clay
loam 2
P-6 99.7
24 Sandy
clay
loam 11
Measured percolation rates are rapid for the soil textures in which
the percolation tests were run.
The City of Orono requires at least three feet elevation difference
between the bottom of the filter rock of a septic system and ground
water or indication of periodic soil saturation such as soil mott-
ling. To meet this requirement, a mound septic system is recom-
mended at this site.
The mound is designed to serve a three bedroom house. Design
sewage flow is 450 gallons per day. With a design infiltration
rate of 1.2 gallons effluent per square foot per day for the medium
sand fill material of the mound, the required rock bed area of the
mound is 375 square feet.
450 gal/day = 1.2 gal/ft2/day = 375 ft2
A rock bed 10.0 feet wide by 40.0 feet long provides the needed
area. A minimum of one foot (1.0l) of medium sand should be
constructed below the rock bed.
The pressure distribution system of the mound consists of Schedule
40 PVC plastic pipe. The supply pipe should slope back towards the
pumping chamber so that it drains after the mound is dosed. The
laterals are 1.5 inch inside diameter pipes. The laterals should
have 1/4 inch diameter holes drilled at a spacing of 3.0 feet. The
laterals should be assembled to the manifold so that the holes
point downwards into the rock bed. The distal ends of the laterals
should be drilled horizontally in the end cap near the crown of the
pipe to facilitate air venting.
A submersible effluent pump capable of delivering at least 30
gallons per minute against a total dynamic head of at least 12.3
feet should be selected. Headlosses are calculated as follows:
1. Vertical headloss of 6.7 feet between pump discharge (approx.
elev. 95.0) and manifold (approx. elev. 101.7)
2. Friction loss of 0.5 feet in 30 feet of supply pipe (1.6 feet
per 100 feet 2.0 inch inch I.D. plastic pipe at 30 gpm flow),
3. Friction loss of 0.1 feet in pipe fittings equal to 25 percent
of friction loss in supply pipe,
Mr. Jim Johnson
May 5, 1987
Page Three
4. Five feet (5.01) to account for losses in distribution network.
If as -built elevations are different from those above, headloss
should be recalculated to ensure proper pump selection.
The pump should be rigged with mercury float switches to dose about
120 gallons of effluent to the mound. An additional mercury float
switch should be installed on a separate circuit to an alarm device
to warn of pump failufe. The mercury switches should be rigged to
allow 450 gallons --.;.serve capacity in the pumping chamber. All
electrical connect j s should be watertight.
The two septic tanks should have at least 1000 gallons capacity
each. The pumping chamber should have at least 1000 gallons
capacity.
It is recommended that a water meter be installed to monitor water
use. The meter should be hooked to the water system such that
exterior sillcocks are excluded. The water meter should be read
periodically to ensure that the design capacity of the septic
system is not exceeded.
It is highly recommended that the installer of this septic system
holds an Individual Sewage Treatment Systems Certificate for
installation issued by the Minnesota Pollution Control Agency.
The sole purpose of soils data contained herein is evaluation of
soil suitability for on -site absorption of septic tank effluent at
the test site. Although soil texture and horizonation information
and groundwater elevation data may be helpful for the setting of
basement elevations at this site, we cannot warrant any such inter-
pretations or use of this data for other purposes.
If you have any questions about information contained in this
report, please feel free to contact me.
Sincerely,
HAKANSON ANDERSON ASSOCIATES, INC.
Gary J. iftfithbun, Soil sc ent st
/ckl
Enclosures File: 1601.01
LOGS OF SOIL BORINGS
PmEc'; Johnson site Evalution FILE No. 1601.01
BmINIG ME11 : _ 4" Flight Auger . _ DM: 5 4 87
DEPTH 0.0
1.0
1.5
2.0
5.0
7.0
Borehole #1
Pi m rfm .. 49.5
Dark brown sandy loam to
sandy clay loam
Dark grayish brown sandy c a
loam, moist
Grayish brown sandy clay,
few yellowish brown mottles,
Grayish brown sandy clay,
many yellowish brown mottles,
many gray gleyed areas, mols'
Gray sandy clay, many
yellowish brown mottles,
many gray gleyed areas, wet
END OF BORING
Ground Watar not anrniintAraA
DEPTH
(feet) 0.0
0.5
1.0
1.5
1oi st
2.5
7.0
Borehole #2
Fr cvarrrw — 99. 9
Dark brown sandy loam
Grayish rown sandy loam to
fine sand
Grayish brown sandy clay
loam
Brown sandy clay loam
Grayish brown sandy clay,
many yellowish brown mottles
many gray gleyed areas
END OF BORING
Ground water not encountered
BY:
LOGS OF SOIL WURINGS
PROEcr; Johnson Site Evaluation FILE No. 1601.01
BORING METHOD: 4" Flight Auger DATE; 5/4/67
3.0
7.0
Borehole #3
M cveTtrw - 100.9
Dark brown sandy loam to
sandy clay loam
Dark grayish brown sandy
clay loam
Brown sandy clay loam, moist
Grayish brown sandy clay
loam, few yellowish brown
...ottles, moist
Gray sandy clay, many
yellowish brown mottles,
many gray gleyed areas
END OF BORING
bround water not encounterea
FWJ AU1iSON =IATES, INC.
(feet
0.0
1.0
2.0
2.5
4.0
6.0
7.0
Borehole #4
Pi cverrnu - 98.0
Dark brown sandy loam
Dark grayish brown sandy
clay loam
Brown sandy clay loam
Grayish brown -sandy clay,
many yellowish brown mottles
many gray gleyed areas
Grayish brown clayey sand,
many yeliowish brown mottles
many gray gleyed areas,
moist to wet with depth
Grayish brown silty clay,
many yellowish brown mottles
many gray gleyed areas, wet
END OF BORING
* Ground water at elev. 91.8 on 4/24/87
BY: 'IQ It It It r
au
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1 •1. ...t�-'^' .'1. _ -_. _St y"j r"`F'+:i.
LAGS OF SOIL BORINGS
PROJECT: Johnson Site Evaluation FILE N0, 1601.01
&AINIG i'ET1i0O: _4" Flight Auger DATE: 5/4/81
2.%,
6.0
8.0
.Borehole #5
FI t:VATTn;d -OA 7
Dark brown sandy loam
Dark grayish brown sandy
clay loam
Brown sandy clay loam
Grayish brown sandy clay loan
few yellowish brown mottles
Gray sandy clay, few
yellowish brown mottles, few
gray gleyed areas
Grayish brown sandy clay to
clayey sand, many yellowish
brown mottles, many gray
gleyed areas, wet
END OF BORING
Groundwater not encountered
HAKA= MUM ASSOCIATES, INC.
DEPTH
(feet)