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HomeMy WebLinkAbout1985-08-26 Septic System Design ReportSYSTEM DESIGN FOR GAPY RODERICK OF LOT 5, BLOCK I, RINGERSWOOD 1 . Percolation Rate, Type of System 35.0 minutes per inch on the primiry site(holes 3-4) and 50.0 MPI on the alternate site(hol,�s 1-2). Mound systems. 2. Propos'(. Flow Rate. 4 bedroims @ 150 G.P.D. = 600 G.P.D. 3. Soil T-eatment Area Needed. 600 G.P.D. x 0.83 factor = 500 Sq. Ft. of rock bed area, or a bed 10 feet wide by 50 feet long. 4. Septic Tanks & Distribution System. Two septic tanks of at least 1000 and 750 gallons, respectively, are needed. In add?tion, a third pumping tank and pump are need- ed for pressure distribution to the mound system. Distribution to the rock bed is to be through 3 perforated laterals 40" apart. All materilas and construction should adhere to the applicable provisions of the city of Orono. 5. Mound Dimensions. Since the ground slope is just a little over 3% only the down - slope area can be used for absorption. The required basal width is 2.4 x 10 or 24 feet which means 10 feet for the rock bed and 14 feet on the downslope side. With a 4:1 sideslope and a 3 foot high mound, the downslope distance would be 13.2 feet so the use of 14 feet is sufficient. Use 4:1 sideslopes on all other sides. If any other information is needed, please contact me. Sincerely, PERCOR, /INC. Mark S. Gronberg, E. PCA certified 0 d- p,4 rF .• P-zc-Ps rrd1. if .. / 4': yo' G,ll� Y /Poo E/P / C /(� oT S gC6ok- 250.00 S 88000' 43" o; i ufi/if cno' �roi i/ r--- I /�2/� NoIE'��OP�CU/4�/o/! �c"S�S L�Tf D��✓� 16 020.E i�y EF sd. X 'O,y1 r.+tiks liol„ o i cos va h Ply\ `N ft i oowoo i Ole, L I � II In I :..7g of Soil Boris is-18 ��� L� Lonation or 1'rojec[ Borings made by f �" ( �.ci-__�;.: N rf-�: i.(_ Date Classification System: AASHO USDA-SCS < Unified : other — Auver used (check. two): Hand X or Power �; Flight or Bucket other Depth, Borin➢. n+amber —I Depth, Borinp number - 2 in Surface elevation in Surface elevation feet feet n_ -.— - ----- n — - — —.•... - 1 — 2 4 — 5 — F — 7 — A — . (' C/J Y %%)A I" End of boring at 7 feet. Ftandinit Water table' Present at feet of depth, _ $,ours after boring. Not present in boring hole X `tottled soil: Observed at fee: of depth. Not rr->sent in boring hole Obs, rvations and comments: 2 — 3 -- 4 6 — 7 — 8 — l�✓ C s /�.t �/ y �' !� f S -i i i i AA - End of boring at feet. Standing water table: ` Present at feet of depth, !.ours after horin;t. Not present in borin- tole PIottled soil: observed at feet of depth. Not present in borin` hole Observations and :omments: b- 33 TEACOLAT10N TEST DATA SKM Test hole location G. v�'r� &;le number Date Lest hole was prepared P 1 2 -� Depth of hole bottom, /er inches. Diameter of hole, 6 inches. Soil data"from test bole: Depth, inches O - /9 /D • /d' Soil texture 194,4 e K ! 1,4 tv% Method of scratchint sidevall _od-10ef I_CKArr/I Depth of pea -sized gravel in bottom of hole, 2 inches. Date and hcur of initial water firing 3y 40-23 -PS Depth of initial water filling, / 6 inches above hole bottom. Mcthod used to maintain at least 12 inches of water depth in hole for at least 4 hours OV $-? y ",014 L-00 A n o,v Percolation test readings made by on _ n g at _�' %S a'fl' startMaximum water depth above hole bottom �,�-- (date) --� during test, inches. 'ime Time 1 inter -,-al, Measurement, Drop in water v:nutes i inches level, inches Percolation rate, j minutes per j inch Remarks P LITi U A ' � �Y Percolation rats w 'YC• 0 minutes per inch. o- aj PERCOLATI0N TEST DATA SHEET Test hole location /C �y!�'� '` Hole number = l Date test hole was prepared'PS Deptb of hole bottom.`,? inches. Diameter of hole, 6 inches. Soil data from test bole: Depth, inches o -p' F -/,p Soil texture f?L.4 rK e o f t", ,,Y1 A re rl,, Y l o " Method of tzrat-hinR sidevall Dtpth of pea -sized gravel in botto= of hole, inches. Date and hc•sr cf initial water filling Depth cf initial water filling, inches above hole bottom. Mcthod used to maintain at least 12 inches of water depth in hole for at least 4 hours Percolation test readings made by on starting at elm. . Maxim= water depth above hole bottom (date) during zest, inches. i '-me Time i :nte-ti•c:, `leasuremcnc, Drop in water Minutes inches level, inches Percolation rate, minutes per inch Remarks .�• ilo/ Percolation Tate • :.fU . -=� minutes per inch. 0- JJ PERCOLATION TEST DATA SHEET Test hole location Solt number Date test hole was prepared Depth of hole bottom,_.�R inches. Diameter of hole, 05 inches. Soil data from test bole: Depth. inches 0-4 /O - iY Soil texture &. e K 60A ih dl4rkl rZAY' 6P,4111 Method of scratching t Depth of pea -aired gray._ bottoz of hole, inches. ;gate and hcur cf initial water filling Depth c_` initial water filling, _ inches above hole bottom. Mcthod used to maintain at least 12 inches of water depth in hole for at least 6 hours Percolation test readings made by on a.m. starting at M. . Maximum water depth above hole bottom (date) during test, _ inches. i = .me i I Time i ;nter1 al. ! HeafiU7Cmen;, Drop in water minutes inches I level, i-^hes I Percolation rate, minutes per inch Remarks 't I le, Percolation rate • el0. =) minutes per inch. a- J� PZRC01.AT10N TEST DATA SKM- Test hole location / 9�;e � cc � Sole number_ Date test hole was prepared e*-11_ - 9 5 , Depth of hole bottom,-/'r inches. Diameter of hole, 6 inches. Soil data from test bole: Depth, inches Soil texture �fc.�rR r!i!Y eOAI�t Method of scratching sidewall Depth of pea -sized gravel in botto= of ho_e, inches. Date ane hc::r of initial water filling Depth c_` initial water filling, inches above hole bottoc. Method used to =aintain at least 12 inches of water depth in hole for at least 4 hours Percolation test readings rade by on starting at 8.m. Maximum water depth above hole bottom (date) during test, inches. i j 7 ime ; 'lime i ;nte1 Measurement, Drop in water Minutes i inches level, inches Percolation ra_e, { minutes per inch Remarks 3 I '8 3"2 •r Percolation rate 0 �=%. 0 ainutes per inch. Lot 2, Block 1 Peres PB21 thru PB:5. Borings BB21 thru BB23. Average• pert s for bath Frimary and alternate sites are. acceptable. SloI)cs nearly level at the tested sites, ranging from 0 to 3%. Mottling indicated below 21, with actual water tab.e at 3.2 to 4.21. A standard mound system should be used due to the presence of sh-illow saturation zones. Lot 3, Block 1 Peres PB31 thru PB26. Borings BB31 thru BB33. Slope, in the primary site are approximate?y 6-88, on a slight flattening Of the 10-121 slopes surrounding it. Borings in the primary site indicate 1 to 2 ' of loamy topsoil over a 6" layer of organic clay topsoil over r. plastic sandy clay. Actual water table at the primary site was bel, 5'. However, the high plasticity indi a heavy clay that i bably saturated. The secondary site mottled below 1.5 '- an actual saturated zone at 1' depth. Coupled with a s. the secondary site i3 marginal for a round system and a .ire at least 2' of sand base as part of the design. I suq�, hata standardpresaure mound system be required for .both sites with addea sand depth fur the secondary system. Please note that this lot is the most tenuous in the subdivision in terms of slope and soils consideration for using a mound system. Should a propo:��d house location encroach on either of the tested sites, careful review and possible additional +.esting will be neeled to ensure that a mound can still be used. rnu site does not appear capable of supporting any kind of a trench system. Lot 4, Block 1 Peres PB41 thru PB46. Boring- 9B41 thru BB43. Slopes average 58 - 7% overall. Borings indicate actual water table at 4' with mottling at a depth of 3-4' for the primary and 2' at tn, --condary site. Perc rates were fairly uniform throughout these tested .sites. A depression/drainageway to the immediate south of the tested sites must be avoided during construction of the systems. I .could recQMQ&g9 A standard pressure mound for both site. Lot 5, Block 1 Peres PB51 thru PB56. Boring:, BB51 thru BB53. dopes are 3% to 6% overall. Mottling at the primary site started at 2.7 to 3.5' with actual water table at 3.7 to 5.0'. This site is acceptable for a standard mound system. The alternate site hag a perc rate considered too slow for any system by code. However, close scrutiny shows that the peres were taken at depth in the sandy clay subsoil, not in the topsoil. In general, throughout the entire subdivision the testing done at a depth of 12", in the topsoil, indicates acceptable percolation rates, with testing at 24" or more indicating slower, marginal perc rates. In my opinion, this site is no different than most of the others, and would have an acceptable perc rate if tested at the 12" depth in the :.andy loam topsoil. No further testing should be required; a mound system if; recommended. ' r= • 414 o / s J N � � w o 00 O o m ---``--t- -- / a n c� I 0 SYSTEM DESIGN FOR GARY RODFRICK OF LOT 5, BLOCK 1, RINGERS;JOOD 8-16-85 1. Percolation Rate, Type of System. 14 MPr on the primary site and 148 MPI on the alternate site. Since the ho•ise is located on the primary site, the alternate site will need to be used. Percolation results were obtained by others and a rate of 148 would not normally qualify for a mound system. However, it was noted that this area was tested at a greater depth and thus if the upper layers were tested, a much better rate would be obtained. 2. Proposed Flow Rate. 4 bedrooms @ 150 C.P.D. - 600 C.P.D. 3.Soil Treatment Area Needed. 600 C.P.D. x 0.83 factor is 500 Sq. Ft. of rock Led area, or a bed 10 feet wide x 50 feet long. 4.Septic Tanks d Distribution System. Two septic tanks of at least 1000 gallons and 750 gallons are needed. In addition, a third pumping tank and pump are needed for pressure distribution to the mound system. Distribution to the ro^_k bed is to be through 3 perforated laterals 40" apart. ,.11 materials and construction should adhere to the provis;o.:s of the Ci�y of Orono. 5. Mound Dimensions. Since trip ground slope is from 2-3i both the upslope atjd downslope areas can be used.Unless additional percolation tests are perform- ed, ar. extra 1 foot layer of sand or 2 feet total should be used to insure adequate percolation in the upper two feet. The required basal width is 5.0 x 10 feet rock bed width or 50 feet. _Thus, the total width of the upslope and downslope must be at least 50 feet minus 10 feet or 40 feet. With a 4 foot high mound, this would amount to _greater than z 4:1 slope. If anything eles is needed, please contact me. Si nr•erel y, PERCOR, INC. Mark S. .,ronberg, F. PCA Certifird — 250.00 S 88000' 43" E _ o� c.t�/i � and di-ei�a9e �orc mew lC / I /vo f2 � PPrcU,�4 •'loll �e�s �S � D�.�� �o • ae 53 �� G l , 1`orF �o PH s \ ` 9495:2 I O PB S-/ I"S iq, o pa T2 0.4 t a 1 I p I N 4A re,. p-lf,pS ,5CALf : / Z/D" SUGGESTIONS FOR REGULAR MAINTENANCE OF SEPTIC TANKS WHAT IS IN MY BACKYARD AND HOW DOES IT WORK? Most houses built in Orono after 1460, where city sewer is not available, have two septic tanks, one or more distribution boxes and a number of drainfield trenches. In the septic tanks, heavy sewage solids will settle to the bottom and be decomposed by anaerobic (oxygen -free) bacterial action. Floating solids such as grease, fat, and :oap scum will be retained inside the tank by baffles at the inlet and outlet. In many cases, the first tank will retain most of the solids and the second tank merely provides extra settling time. This ensures that'the effluent entering the drainfield is relatively free of solids which tend to clog up clay soils. TYPICAL SEPTIC SYSTEM ►iA5 EM ENy Floating r= ��19 T r., -_� -. _.T -.� �.- -., Solids a Sludge Distribution Box Lrainfield WHY BOTHER WITH PREVENTIVF MAINTENANCE? Eventually, a septic tank that is functioning rnrrectly will accumulate a large quantity of sludge (decomposed wastes) and floating solids. If this accumulation is not removed regularly, the solids will by-pass the baffles in the tank and will ;)e flushed out into the drainfield causing premature and unnecessary clogging of the drainfield. The result: sewage will ba(-k up into your house and;or form a puddle (or river) jin your yard. THERE ARE NO INEXPENSIVE WAYS TO R.PAIR A CLOGGED DRAINFIELD, M M �, c- 77�' c) -7q sb M 6 zL >:s r �o�rzr:-►Hw► � 7 D 7 (� D •rf O 0� zy •-8 r t 1 30 N , j �?41 / 2 N E,j' `�,��ij- ru •• � , i � .t �_ � hnr �'Q 5 R e, ... . C M rs As AID ; rr.d r/ M 4W I HrrAtil 31 Cow x.w.. 4 Am) w 10 y g� L lit FDN6~� s I w �, 7'';� /Z�wIP \MP \ �l� 2 �1 _ S ' i G 1 psi 21' N� Mod 3 a1R \� / N7H• —1 FboJ ONLm [• L II "CMP I /?~GMI� �1+: i� �� •i' s �4�j �� •� �•.. , nr Af Jel �'? / _ C c � v rr t ► �G'� mac.. 2 j l TLOT A VIEW A. 0 b — — u s. Ma w, hp� *,w AA °4 VIL OF LONG LAKE' IssI oo V •.•rr �•- q� Or r C, K2-1 cv�'- 8225 8224 3so Y2�4 Tq o � •�o 2 �31 4 h. 8110 yisoets �� . , — - ISO 50 v' Vetid •d dt�Vv�'V �cvmfAMve mx�zm�aprr�a+'s+pmn'rnno _(Pm(Pt_P�_ Al ut to o t/1 J s t s W �y W N cN 1y r . NJ . ,�� ^� N S r• All i• �►r N 1.A (i+ r —. p �� �u �� U v1l- lV - .1 1i 1 �IV J! � i J•. r: L j w � �; w '+ 4 ' J1 i !J. s N t ! � N N Z _ atos� L a � ✓ y 0 tl��v-vvv•vvvvvvvv-o-vG f>_s_s_>>_a_•s_�fvo�waovo� isi$ �'$ vve? wamCID {� (t r• N ii� 1` W ►`� N CO J O• U� •� W rJ �. W -.all� to N ;� a r: L fi cr w ? iu ` :7 ` c j 3N wj l�Ntfa i d 0 3 1_ A 0 MAR RXrxr7Jii�isr7f'-V' N N ri rj vp a, v► C� 0. o• f r to A w f Jl 0 � � r 4• ♦ W P+ � i W = I` N �' tad N � O` f 1� {` W r, T lh � w �� — � � N ` t r w : a • HOW CAN I MAKE MY DRAINFIEI_D LAST LONGER? Here are a few suggestions: -Don't use ;►our toilet or kitchen sink as a garbage can. Undigested foods and cigarette butts will not decompose in the septic tanks. -if you have a garbage disposal use it as seldom as possible or not at all. -Have your tanks pumped at least once every three years to remove the solids. '"his will probably cost $ 75.00 - 100.00. If you don't specifically ask the pumping contractor to open up your tanks, he will probably just put his hose down the inspection pipe and drain the liquid from the tanks. This method does not effectively remove solids. He should open the tanks, stir the contents while pumping to break up the sludge and scum layers, and at the sLme tims clean and repair or replace baffles as necessary. Baffles have a bad habit_ of falling off aFter a number of years. -You should also open up the distribution box and remove any accumulated solids. HOW CAN THE VIIIAGE HELP ME MAINTAIN MY SYSTEM? The septic system inspector will come around at least once every two years to measure the accumulations in your tanks and evaluate the overall system condition. You should have at least one 4" diameter inspection pipe extending to the surface from each tank for easy inspection access. Every licensed contractor sends a pumpout notification slip to the Village when a tank is pumped. The Village keep_ an inventory and inspection/maintenance record card for each septic system and will send out a notice to the homeowner when a requAred maintenance pumping (once every three years) is overdue. If you have questions or problems with your septic system, feel free to call the inspector a:. 473-7357. fA r GA U U) to w '.o Ln iI tj r+Ull r A y r R' 14 r' ' R 1'. F ' J i n 1r1 f 1' i t Iri r _ ` tL) s • � r �' N .• �' VI e o• A i vl � r f .c .1 rNi a i► w " Jr. i l 1� t' Ito yl s ^ q •' �, to ^' O r� U' d ._, J 4•, YI J V r/ � , � � � -•. � � �r .<� 1 L gin; r 01 na •ri S�n E� J s�V / � ;A , it it tc,1 It 100 0 r+ ell 0 p / N W EXH!91T November 27, 1981 P.O. Pox 209 Wayzata, Minnesota 55391 Mr. Judd Ringer 405 South Willow Drive Long Lake, Minnesota 55356 Dear Mr. Ringer: We have completed a site evaluation for on -site sewage treatment facilities of 15 proposed lots located East of Willow Road and North of Trunk Highway No. 12 in Orono, Minnesota. A location map has been enclosed showing the location of the soil borings and percolation tests. Soil boring logs and percolation test data is also enclosed. The soil boring show a uniformly high water table throughout the area tested. This condition prohibits the installation of conventional soil absorption systems. The gentle slopes and percolation rates encountered indicate that Mound Systems should be satisfactory on these sites. We recommend that the future homes be provided with Mound Systems of soil absorption. Please call if you have any questions. Thank you. Yours very truly, CARL W. BORG, P.E. el \ CWB:vl cc: Mr. Michael Gaffron City of Orono Ene. 3 copies - Location Hap Sheets 1 - 3 - Soil Borings 1 Sheet Percolation Test Data #615 Ringer Subdivision Page 6 Lot 6, Block 2 Peres PA61 thru PA66. Borings BA61 thru BA63. Slopes are nearly level. Mottling occurred below 1.5', with actual water encountered below 5.71. (Note that soil appears saturated below 2.51) Perc rates were acceptable, although 1 of 6 taken at depth very very slow. Both primary and secondary sites should use mound systems. Lot 1, Block 3 Peres PCll thru PC14. Boring BC11 and BC12. This lot contains an existing house, garage and barn. The existing septic system is unknown and was not located during my routine inspection in July 1981, although no evidence of failure was noted. A future drainfield site has been tested to the south of the house. Average percolation rate is 21 minutes per inch; soil borings indicate soils suited for a shallow trench or mound system, with mottling beginning at a depth of 5'. This is the highest elevated point in the entire subdivision and appears to be the only lot possibly suited for a shallow trench system. An attempt should be made to locate the existing system to ensure it is within the lot boundaries, although there is only a•remote possibility that it isn't. Lot 2, Block 3 Peres PC21 thru PC24. Borings BC21 and BC22. This lot contains an existing house and small shed. The existing septic system is unknown and was not located during my inspection last July. No evidence of system failure is noted. While the existing system undoubtedly consists of trenches, soils data provided for a future drainfield site indicates mottling at a 3.5' depth. This indicates that the replacement system, should it ever be necessary, would probably have to be a mound. Percolation rates averaged 56 mpi. It would alto be advisable to locate the existing system to ensure it is within the new lot boundaries. B. Discussion of Mound Systems Since the proposed Ringer subdivision appears to need mound systems throughout, it might be worthwhile to review the conditions which favor use of mound systems over conventional trench systems. As you are aware, a biomat forms at the rock -soil interface in a standard trench system. This biomat acts as a "valve" to slow the downward percolation of septic tank effluent to a rate where the flow is unsaturated, i.e. air in the soil pores is in contact with the percolating effluent. Under these essential conditions, adequate sewage treatment will occur. However, in many soils, either a seasonal saturated condition or extremely fine, impermeable soil texture (or both) tends to eliminate the air/effluent contact and also severely limits the soils capacity to absorb large amounts of effluent. To ensure that a standard trench system is not • #615 Ringer Subdivision Page 5 Lot 6, Block 1 Peres PB61 thru PB66. Borings BB61 thru BB63. Average perc rates at both sites are acceptable. Slopes range from 2 to 4%. Mottling started at a depth of approximately 2.4 feet, with actual water level at 2.5 to 4.41. A standard mound system should be used at both sites. Lot 7, Block 1 Peres PB71 thru PB76. Borings BB71 thru BB73. Slopes average 2-3%. Perc rates were fairly slow, with the secondary site being somewhat slower than the limit (however, the justification for Lot 5, Block 1 also applies here). Actual water level ranged from 1.7 to 3.5' with mottling generally below 2.51. A standard mound is recommended for both sites. Lot 11 Block 2 Peres PA11 thru PA18. Borings BA11 thru BA13. Slopes are very flat. Mottling was indicated below 2.2 ' with actual water encountered below 2.01. Two secondary sites were tested. All sites are acceptable for a standard mound system. Lot 21 Block 2 Peres PA21 thru PA26. Borings BA21 thru BA23. Very flat slopes. Mottling occurs at 2.0 to 2.4' with actual water encountered below 2.41. Perc rates on both sites are acceptable. A mound system is recommended for both sites. Lot 3, Block 2 Peres PA31 thru PA36. Borings BA31 thru BA33. Slopes averaged 2 to St. Mottling starts at a depth of 2.0-3.51. Actual water level was below 2.51. Perc rates are acceptable. Mound systems are recommended for both sites. Lot 4, Block 2 Perce PA41 thru PA46. Borings BA4 flat. Mottling generally was four water level at about 4.01. Perc r acceptable; perc rate for secondary acceptable for a mound based on th for Lot 5, Block 1. I recommend a Lot 5, Block 2 1 e thru BA43. Slopes are very d below 2.01, with actual ate for primary site is site is slightly slow but justification referred to mound system for both sites. Peres PA51 thru PA56. Borings BA51 thru BA53. Slopes are very flat. Mottling occurred below 1.2 feet with actual water below 4.0 feet. Perc rates are acceptable for the primary site and slightly slow at the secondary site. (Refer to Lot 5, Block 1) This lot has the overall worst set of percolation rates of the division. 'However, only two of the peres were taken in the topsoil, the others, two of which were very slow, were at depth. I recommend that a mound system be used on this site. If peres were re -taken in the topsoil, it is likely they would pass as did nearly all others done in this manner. #615 Ringer Subdivision Page 4 Lot 2. Block 1 Peres PB21 thru PB26. Borings BB21 thru BB23. Average perc rates for bith primary and alternate sites are acceptable. Slopes are nearly level at the tested sites, ranging from 0 to 3%. Mottling indicated below 2', with actual water table at 3.2 to 4.21. A standard mound system should be used due to the presence of shallow saturation zones. Lot 3, Block 1 Peres PB31 thru PB29. Borings BB31 thru BB33. Slopes in the primary site are a;,,.oximately 6-88, on a slight flattening of the 10-12% slope& surrounding it. Borings in the primary site indicate 1 to 2 ' of loamy topsoil over a 6" layer of organic clay topsoil over a plastic sandy clay. Actual water table at the primary site was below 5'. However, the high plasticity indicates a heavy clay that is probably saturated. The secondary site was mottled below 1.5 feet with an actual saturated zone at 1' depth. Coupled with a slope of 10% the secondary site is marginal for a mound system and would require at least 2' of sand base as part of the design. I suggest that a standardpressure mound system be required for both sites with added sand depth for the secondary system. Please note than this lot is the most tenuous in the subdivision in terms of 31ope and soils consideration for using a mound system. Should a proposed house location encroach on either of the tested sites, careful review and possible additional testing will be needed to ensure that a mound can still be used. The site does not appear capable of supporting any kind of a trench system. Lot 4, Block 1 Peres PB41 thru PB46. Borings SB41 thru BB43. Slopes average 5• - 7t overall. Borings indicate actual•water table at 4' with mottling at a depth of 3-4' for the primary and 2' at the secondary site. Perc rates were fairly uniform throughput these tested sites. A depression/drainageway to the immediate south of the tested sites must be avoided during construction of the systems. I would reC M apA tandard pressure mound for both sites. Lot 5, Block 1 Peres PB51 thru PB56. Borings BB51 thru BB53. Slopes are 3% to 6% overall. Mottling at the primary site started at 2.7 to 3.5' with actual water table at 3.7 to 5.01. This site is acceptable for a standard mound system. The alternate site has a perc rate considered too slow for any system by code. However, close scrutiny shows that the peres were taken at depth in the sandy clay subsoil, not in the topsoil. In general, throughout the entire subdivision the testing done at a depth of 12", in the topsoil, indicates acceptable percolation rates, with testing at 24" or more indicating slower, marginal perc rates. In my opinion, this site is no different than most of the others, and would have an acceptable perc rate if tested at the 12" depth in the sandy loam topsoil. No further'testing should be required; a mound system is recommended. 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A 0- CD � � 941 r•r• N I"r m N -ova 'da ww 1-0 t-• m � � 44 ww s ut %o %D � � 'da ww ut N w � 8 44 r•w K aw rtA A� n a ~ o a �rt0A r • (+ p- Nt•+W NW rW NA NAP Nw Nw w A M a a a h~+ A r O A a• r A m O � O a w A A 00 i t N NW 000 11 1 N N N 1 N W N 1 N �P N 1 W at usol I I -I m mob t l C tT o0 1 1 N W 00 I I W wO a C K log 41 f M • K• O a rt rt O W MM rtrt N N 1 NJ PAPA rtrt N N ulut MM rtrt tJ N NA PAPA rtrt N N O:I MM r+rt N N Om Ph t•+rt of tAM rtrt N N ON MM rt rt /-r N vO MM rtrt fo rrtt w rt a C a a la-• � 66 G G as 669 G G G aaa Re G� as 96 G G a.a Re G G as 66 G G as Re G G as Re � G as Re G G as tAn a A �.1 Z abed: S19t uoTsTATpgng aabuTH • EXhlt31T TO: Jeanne A. Mabusth, Zoning Administrator FROM: Michael P. Gaffron, Septic System Inspector DATE: January 5, 1982 SUBJECT: Ringer Subdivision, North Willow Drive #615 Summary: All proposed lots were found to have high water tables, necessitating the use of mound systems. Percolation rates in the upper soil profile generally were suitable for mound systems, with slower rates found in deeper test holes. Slopes on thn entire site are fairly level and suited for mound systems. This report will consist of: a) a short review of each lot of the proposed division and b) a discussion of mound systems,including how and why they work and their current and future use as part of Orono's land use management plan. The Ringer subdivision is perhaps the most extensive development in Orono to date that will require all mound systems. A. Ringer Subdivision A preliminary review of the Hennepin County Soil Survey indicated extensive areas of Cordova silty clay loam and Shorewood silty clay loam as well as Leseur loam would be found at this site. These soils all would be expected to have a seasonal water table or saturation zone between 1 and 3 feet below the surface. During the course of the soils investigation, I met with the site evaluator, Carl Borg, and realtor-Graydon McCulley on the site. We made a boring which definitely indicated these high water table soils were present. I later confirmed with Dr. James L. Anderson of the University of Minnesota Soils Extension Department that mound systems would be. appropriate for these soil types. These are much the same soils as found in the Medina- 14orningside area, which experience conventional trench septic system failures due to the soil conditions. In general, the loamy topsoil characteristics for the Ringer property are suitable for proper functioning of standard pressure -mound septic systems as per Orono's Code and Design Manual. For clarity's sake I have labeled the northern most tier cf seven lots as Block 1, the western group of six lots as Block 2, and the two lots to the southeast as Block 3. Lot 1, Block 1 Peres PBll thru PB16. Borings BB11 thru BB13. Average perc rates for both primary and alternate sites are acceptable. Slopes are quite level. Saturation indications (mottling) started at 1.7 to 2.5 feet. Actual water table at 5-7' depth. A mound system should be used due to the presence of shallow saturation zones. 9 SEPTIC SYSTEM INFORMATION STREET ADDRESS 750 JNCA:'FY ZAAzAF 17,e/t* LOT S BLOCK SUBDIVISION R/AUGfr-IeS WOOD MONTH AND YEAR TESTING DONE // 6�- NOU• 1961 ITEMS ALREADY COMPLETED _ f0 rfXC 7Z5TS (,Pl3`SI , P6 SZ, PB-S3, -% o% Yr-C% v/C - t L ) S c. I) slwfrIA I r C f sc Az -G I he" - NEED TO COMPLETE BEFORE ISSUING BUILDING PERMIT; OBORINGS OPERC TESTS 0 SYSTEM DESIGN AfQ A-,lD- SITE PLAN O OTHER SUBDIVISION FILE NO. �p�s DATE THIS SHEET FILED BYA& i