HomeMy WebLinkAbout1986-03-06 Septic System Design ReportHakanson Anderson Associates Inc.
222 Monroe Street, Anoka, Minnesota 55303 EuMm J. Hakanan, P.E.
6121427-500 JanM M. Winter, R.L.S.
engineers rs and snrrveyon Lawrence 0. K n ilm , P.E.
Peter R. Reetikka, P.E.
March 6, 1986
VarwEeckhout Building Corp.
Attn: Chuck VanEeckhout
15500 Wayzata Boulevard
Wayzata, MN 55391
Dear Chuck:
At your request a site evaluation to determine soil suitability for an
on -site sewage treatment system was performed at Lot 6, Block 1, The
Nursery in the City of Orono, Minnesota. Standard methods of percola-
tion testing were employed. Elevations are relative to an assumed
elevation of 100.0 based at the center of the Devlin Lane cul-de-sac
(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 silt loam to sandy clay loam topsoils
overlie sandy clay subsoil horizons. A discontinuous silty medium
sand subsoil horizon was encountered at Borehole #1. Soil mottling
and gleying begin at 1.5 to 2.0 feet depth at the boreholes. Soil
mottles (spots of contrasting color) are accepted indicators of
periodic saturation in soils. Gleying (dull gray soil color) form in
soils which are saturated and in a chemically reduced condition for
long periods of time. Ground water was measured at elevation 103.3
and 101.1 at Boreholes #1 and #5, respectively on March 6, 1986.
civil • municipal a planning • soils a laid sureryir a lalkisrape, architecture
t
Mr. Chuck VanEeckhout
Page 2
March 6, 1986
Percolation test results are as follows:
Depth
Soil Texture at Percolation Rate
Hole Elevation
(inches)
Bottom of Hole
(min/in)
P-1
109.8
24
Silty sand to medium sand
1
P-2
107.8
18
Silty sand to clayey sand
15
P-3
107.9
18
Sandy clay
17
P-4
109.1
24
Silty sand
6
P-5
108.4
24
Silty sand
16
P-`
106.1
18
Sandy clay
23
Measured
percolation rates
are consistent to somewhat
rapid for the
texture
of the
soil materials in which the percolation
tests were run.
The City of Orono requires at least three (3.0) feet separation
between the bottom of the filter rock of a septic system drainfield
and groundwater or indication of periodic soil saturation such as soil
mottling. In order to provide the required separation, a mound septic
system design is recommended for both the primary and alternate septic
system sites on this lot.
The proposed mound system is designed to serve a four bedroom house.
Design sewage flow is 600 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 500 square feet.
600 gal/day = 1.2 gal/ft2/day - 500 ft2
A rock bed 10.0 feet wide by 50. a lon ovides the needed area.
A minimum of one and one-half f et (1.5') of m dium sand should be
constructed below the rock bed.
The basal area calculation of the mound is based on a loading rate of
0.45 gallons per square foot per day for silty clay to sandy clay loam
soils. The mound should have at least 1,333 square feet of basal area.
600 gal/day _ 0.45 gal/ft2/day - 1,333 ft2
The basal width of the mound (basal width - distance between upslope
edge of rock bed and toe of medium sand fill) is 27 feet. (See cross
section of mound on enclosed sketch.)
Mr. Chuck VanEeckhout
Page 3
March 6, 1986
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 capped. Also, the last hole in each lateral 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 3
gallons per minute against a total dynamic head of at leas 15.7
should be selected. Headlosses are calculated as follows:
1. Vertical headloss of 10.0 feet between pump discharge (approx.„
elev. 101.0) and manifold (approx. elev. 111.0)
2. Friction loss of 0.7 feet in 30 feet of supply pipe (2.35 feet
per 100 feet 2.0 inch I.D. plastic pipe at 37.5 gpm flow),
3. Five feet (5.0) 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
150 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 failure. The mercury switches should be rigged to allow
600 gallons reserve capacity in the pumping chamber. All electrical
connections should be watertight.
The first septic tank should have at least 1,250 gallons capacity. /
The second septic tank should have at least 1,000 gallons capacity. -Oor
The pumping chamber should have at least 1,000 gallons capacity.
It is highly recommended that the installer of this septic system
holds an Individual Sewage Treatment Systems Certificate for installa-
tion 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 interpretations or
use of this data for other purposes.
0
Mr. Chuck VanEeckhout
Page 4
March 6, 1986
It you have any questions about information contained in this report,
please feel free to contact me.
Sincerely,
HAKANSON ANDERSON ASSOCIATES, INC.
Ghry JWthmn, soil Scientist
/mlc
Enclosures
File: 693.04
• IMS OF SOIL BORINC3S
Pgocr: VanEeckhout Percolation FILE No. 693.04
BMING MEd: 4" Flight Auger WE: 3/6/86
(feet 0.0
1.0
2.0
4.5
6.5
7.5
Borehole 01
F� wart nu - 109 -A
rk brown silt loam
Brown sandy clay loam
UfAyish brown silty medium
and
rayish brown silty medium
and, few to many yellowish
rown mottles, few gray
leyed areas, wet to saturate
/depth
Gray silty clay, many
yellowish brown mottles,
many gray gleyed areas, wet
END OF BORING
*Ground water at 103.3 on 3/6/86
0001 NWW1 ASSOCIATES, INC.
E3
OEM
feet 0.0
1.0
1.6
3.0
7.0
Borehole /2
1:1MATIAM -1W_A
Dark brown silty clay loam
Brown sandy clay loam
Grayish rows silty c ay oam
any yellowish brown mottles,
any gray gleyed areas
Grayish brown sandy clay, few
yellowish brown mottles, few
gray gleyed areas
END OF BORING
Ground water not encountered
BY:
LAGS OF SOIL BORINGS
Roza: YanEeckhout Percolation FILE N0, 693.04
DING NM; 4" Flight Auger DATE: 3/6/86
c,
(feet)
O.Q
1.0
1.5
M
4A
7.1
Borehole /3
G e%&A"Au — -I n-v a
Frkb silty clay loam
y clay loam
own sandy clay
loam, many yellowish brown
mottles, many gray gleyed
areas
Brown silty sandy clay, few
yellowish brown mottles
i
Grayish brown silty sandy
clay, many yellowish brown
mottles, many gray gleyed
areas
END OF BORING
brouno water nuL enwunr,cu
NAKAIMI At+DOR9(XV ASSOCIATES, INC,
Borehole #4
p� y �. H rv1Tl�l — 1[�8
( :-et) Dark brown sandy lom to
sandy clay loam
1.
Gray silty clayey sand, wet
2.
Gray silty clay, many
yellowish brown mottles,
many gray gleyed areas, wet
4. -
Gray -'silty clayey sand, many
yellowish brown mottles,
many gray gleyed areas, wet
1.
END OF BORING
Ground water not encountered
BY:
I= OF SOIL BORINGS
Fpp,ECT; VanEeckhout Percolation FILE No. 643.04
BMINS "EnM; 4" Flight Auger DATE: 3/6/86
OEM
feet)0.0
1.0
1.5
3.0
6.0
Borehole #5
Fi euari nr - I n6.1 .
Dark brown sandy clay loam
Brown sandy clay loam
Grayish brown sandy clay,
many yellowish brown mottles,
many gray gleyed areas, wet
Gray silty sandy clay, many
yellowish brown mottles,
many gray gleyed areas
END OF BORING
*Ground water at 101.1 on 3/6/86
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