HomeMy WebLinkAboutWetland info � _ <<�-23- 13-oe�.3 ,
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Minnesota Wetland Co servation Act I
�
Notice of Appli ation
Local Government Unit(LGU) Address
Minnehaha Creek Watershed District 15320 Minnetonlca Blvd
Minnetonlca,MN 55391
1. PROJ�CT INFO TION
Applicant Name Project Name Date of Application
VCI Capital Lalce Lot Adjacent t 4245 Application Number
Bayside Road 10/14/2013 W13-43
Ci of Orono
T e of A lication check all that a 1 :
�Wetland Boundaiy or Type ❑No-Loss Exemption ❑ Sequencing
❑ Replacement Plan Banking Plan
Summar and descri tion of 1•0 osed ro'ect attach additional heets as necessai ):
VCI Capital has applied for a wetland bouudaiy&type approva for the parcel located at a lalce lot adjacent to
4245 Bayside Road in the City of Orono.Thc complete applicat on was received on October 14,2013.The
delineation was performed by Svoboda�cological Resources o October 8,2013.The boundai•y will be
reviewed in the field by MCWD staff.
2.APPLICATION I2�VI�W ND DECISION
Signing and mailing of tliis completed form to the appropriate •ecipients in accordance with 8420.0255, Subp.
3 provides notice that an application was made to the LGU ui der the Wetland Conservation Act as specified
above. A copy of the application is attached. Comments can b submitted to:
Name and Title of LGU Contact Person Co ments must be received by (minimum 15
Brandon Wisner bu iness-day comment peciod):
Compliance Officer N ember 13,2013 (4:30 PM)
Address(if diffe�•ent than LGU) D e,time,and location of decision:
15320 Minnetonlca Blvd A decision will be made following the field
Minnetonita,MN 55391 re iew and completion of thc comment period.
Phone Number and E-mai]Address D cision-makec for this application:
(952)641-4505 Staff
bwisner@minnehnhacreelc.org Governing Board or Council
Signature:�,� Date: I Z Z
BWSR Forms 7-1-10 I P�ge 1 of 2
II �
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3. LIST OF ADDItES EES
� SWCD TEP member: Stacey Lijewslci—st�ceylijewski@c .hennepin.mn.us
� B WSR TEP mcmbcr: Lynda Peterson—lynda.peterson@s ate.mn.us
❑ LGU TEP mcmber(if different than LGU Contact):
❑ DNR TEP member:
� DNR Regional Office(if different than DNR TEP member): elissa Doperalslu—
Melissa.Doperalsl�i a state.mn.us
❑ WD or WMO(if applicable):
� Applica�lt(notice only)and Landowner(if different):VCI C pital—i•ob�vl�ite a vcicapit�l.com �
� Members of the public who rec�uested notice(notice only):
Consult�nt: Svoboda Ecologic�l Resources(Erica Britcliei•)—ei•icab@gpsimiovations.com
City of Orouo(Cl�ristine Mattsun)—cmattson(n�ci.orono.mn. s i
� Corps of Engineers Project Manager(notice only): Melissa nny—Melissa.m.jenny@usace.army.mil i
❑ BWSR Wetland Bank Coordinator(wetland bank plan appli ations only) �
4.MAILING INFORM TION
➢For a list of BWSR TEP i•epresentatives:www.bwsr.state.mn.us/ ontact/WCA areas. df
➢For a list of DNR TEP representatives: www.bwsrstate.mn.us/w tlands/wca/DNR TEP contacts. df
➢De artment of Natural Resources Re ional Offices:
NW Re�ion: NE Re�on: Cen r�l Re ion: Southern Region:
Reg.Env.Assess.Ecol. Reg.Env.Assess.Ecol. Reg Env.Assess.F.col. Reg.Env.Assess.�col.
Div.Ecol.Resources Div.�coL Resow•ces Div Ecol.Resources Div.Ecol.Resoucces
2115 Birchmont Beach Rd.NE 1201 E.Hwy.2 120 Warner Koad 261 Hwy. 15 South
Bemid'i,MN 56601 Grand Ra ids,MN 55744 St. aul,MN 55106 New Ulm,MN 56073
For a map of DNR Administrative Regions,see:htt ://files.dm�.s ate.imi.us/aUoutdnr/dnr re ions. df
➢For a list of Corps of Project Managers;www.mv .usace.arm .n '1/i•e ulator Jdefault.as ? a eid=687
or send to:
➢
US Army Corps of Engineers
St.Paul District,ATTN:OP-R
180 Fifth St.East,Suite 700
St.Paul,MN 55101-1678 !
➢For Wetland Bank Plan applications, also send a copy of the app'cation to: I
Mimlesota Board of Water and Soil Resources
Wetland Bank Coordinator '
520 Lafayette Road North '
St. Paul,MN 55155
5.ATTACHMEN S
In addition to the application,list any other attachments:
� Wetland Delineation Report
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❑
❑
❑
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BWSR Forms 7-1-10 Page 2 of2
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�P�roviding the Sharper Edge �n
Natura,l Resources &Enuironmental Conaul��'ng
� ECOLOGICA� RES�URCES �
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Lake Lot Adjac nt to 4245
Bayside Rd
Orono, Hennepin ounty, l�'IN
Wetland Classification, I entification, and
Delineation eport
Prepared for: �,
VCI Capital '
By:
Svoboda Ecological Resources
Project Number 2013-021-03
10/10/2013 I
The contents and format of this report are consi red intellectual property and
are subject to copyright restrictions and may n t be reproduced without
the express permission of Svoboda Ecolo ical Resources.
Table of Contents �
ABSTRACT.............................................................4...... ...............................................................1
INTRODUCTION.......................................................... ...............................................................1
METHODS..................................................................... ...............................................................1
RESULTS...................................................................... ..............................................................2
DISCUSSION................................................................. ...............................................................4
RECOMMENDATIONS............................................... ...............................................................4
CERTIFICATION......................................................... ...............................................................6
DATASOURCES........................................................... ...............................................................7
LITERATUREREFERENCED................................... ...............................................................8
FIGURES:
Figure 1: Site Location Overlaid on Topographic M
Figure 2: National Wetlands Inventory
Figure 3: Web Soil Survey-Hennepin County
Figure 4: Public Waters Inventory
Figure 5: Approximate Wetland Boundary and 3amp e Point Location
TECHNICAL DOCUMENTS:
Photo Log
Field Data Sheets ��
Plant Indicator Status
Soil Series Data
ABSTRAC
Svoboda Ecological Resources (SER) visited the ab ve referenced property on 10/8/13 to
examine the site for the presence of areas meeting wetla d criteria. The study parcel is located in
the ciry of Orono, MN in Hennepin County (Figisre 1). ne wetland boisndary was delinec�ted at
this site. Two sample transects were established, one each along the northern and southern
boundaries of the wetland area in order to charac rize the soil, vegetation, and existing
hydrology within the wetland-to-upland tYansition zone.
INTRODUCT ON
The subject parcel is approximately 12.05 acres and t e target area is dominated by emergent
herbaceous wetland species. The topography of the s te around the target site consists of a
woodland area sloping down to the northeast into the etland with a small water body to the
east. The surrounding land use is primarily widely spac d single family homes while the parcel
itself is close to Lake Minnetonka. The identified w lands were classified according to the
Cowardin et al., the Circular 39 and the Eggers and Ree classification systems and marked with
pink "Wetland Delineation" pin flags. The Technical D cuments section of this report contains
field data sheets, plant indicator status information, soil survey information, and wetland
definition information.
It should be noted that the present delineation does not i clude consideration of the large wetland
in the southwest corner of the parcel. The scope of the d sired project is only close to the wetland
delineated in this report.
METHOD
The methods used to delineate the subject parcel are as escribed in the 1987 US Army Corps of
Engineers Wetlands Delineation Manual and the 2010 �dwest Regional Supplement ManuaL In
the 1987 Manual, the methods used were described u er the "routine" methods for sites less
than 5 acres. This methodology is followed in order to ssess whether the three parameters of a
wetland are met for areas on the subject parcel. The ee parameters required under normal
circumstances in order to delineate a wetland are describ d in the Technical Documents section.
The Midwest Regional Supplement Wetland Deline tion Manual is also being utilized to
increase the accuracy of our wetland boundaries. This dendum to the original 87 Manual was
created to address the many regional differences that aff ct wetlands and the delineation methods
used throughout the country. The following explanation are passages from that document.
"This Regional Supplement is part of a nation ide effort to address regional
wetland characteristics and improve the accura y and efficiency of wetland-
delineation procedures. Regional differences in climate, geology, soils,
Svoboda Ecological Resources 1 4245 Bayside Rd
Project Number: 2013-021-03 Orono,MN
hydrology plant and animal communities, and ot er factors are important to the
identification and functioning of wetlands. hese differences cannot be
considered adec�uately in a single national ma ual. The development of this
supplement follows National Academy of Scienc s recommendations to increase
the regional sensitivity of wetland-delineation methods (National Research
Council 1995).The intent of this supplement is t bring the Corps Manual up to
date with current knowledge and practice in he region and not to change
wetland boundaries." "...This Regional Supple nt is designed for use with the
current version of the Corps Manual (Enviromm �tal Laboratory 1987) and all
subsequent versions. Where differences in th two documents occur, this
Regional Supplement takes precedence over the orps Manual for applications
in the Midwest Region."
National Wetland Inventory (NWI) maps (Figure 2), W b Soil Survey of Hennepin County map
(Figure 3), Minnesota Public Waters Inventory maps Figure 4), and 2012 aerial photographs
were reviewed prior to the site visit to identify areas hat may be wetlands. Areas illustrating
evidence of wetland conditions were examined in reater detail during the field survey.
Vegetation, soils and hydrology were examined (as o lined in the 1987 Manual) and used to
characterize wetland types and determine wetland boun aries. Sample transects were established
in representative wetland-to-upland transition zones in rder to characterize the vegetation, soils,
and hydrology of the site. Transects consist of a r presentative upland sample point and
representative wetland sample point. Information obtai ed at the sample points can be found on
the field data sheets located in the Technical Documents section.
Wetland boundaries were marked at the site by pin "Wetland Delineation" pin flags. The
wetland boundary is considered to be the topographic ly highest extent of the wetland basin;
areas below the staked boundary met the three required wetland criteria while areas above were
lacking in one or more of these criteria. Wetlands wer classified in accordance with methods
described by Cowardin et al. (1979) and used in the N (e.g. PEMB, PSS1C, etc.), completed
by the U.S. Fish and Wildlife Service. The Circular 39 and Eggers and Reed classification
systems are also given. The indicator status of plants, s described in the Technical Documents
section, was determined using the National List of P ant Species That Occur in Wetlands —
Region 3 (Sabine 1999).
RESULTS
The National Wetland Inventory indicates a wetland of t e PEMC in the survey area. (Figure 2).
The Web Soil Survey of Hennepin County (Figure 3) id ntifies six soil map units present on the
subject property. They are as follows: Klossner soils, epressional; Muskego, Blue Earth and
Muskego,ponded; Hamel, overwash-Hamel complex;A gus-Kilkenny complex; and two Lester-
Kilkenny complex types of different slopes. The first t o types are the hydric soils on the site.
The Hamel complex is partially hydric. The remaining Kilkenny complexes are predominantly
non-hydric. Soil series descriptions are provided in the chnical Documents section.
The Minnesota Department of Natural Resources, Sta e Protected Waters Map (Public Water
Inventory) indicates no public waters within the area of i terest on the parcel (Figure 4).
Svoboda Ecological Resources 2 4245 Bayside Rd
Project Number: 2013-021-03 Oronq MN
Site Visit
SER ecologists examined the subject property for are s meeting jurisdictional wetland criteria
during the site visit. One area meeting the jurisdiction 1 criteria of a wetland was flagged, and
boundaries were determined and delineated. The appr ximate wetland boundary is outlined in
yellow (Figure 5). At the request of the client and verb 1 approval of the LGU, only the subject
wetland was delineated. Location of the boundary is n eded in order to accommodate a future
driveway on the as two separate lots are involved ut which may be under two separate
ownerships in the future.
The NWI had previously identified the present wetland as PEMC. The wetland is a depressional
wet meadow with an open pond area that is semi pe anently inundated on the east side. The
open pond area was created by previous excavation and residual evidence of the sidecast spoil is
evident on a recent aerial photo (Figure 5).
The wetland of interest is located in the northern quarte of the parcel. The wetland vegetation in
the seasonally inundated wetland was dominated re d canary grass (Phalaris ari�ndinacea
FACW). The transition to upland can be marked vegeta ively, primarily as the reed canary grass
disappears and the blue grass (Poa pratensis FAC) begi s on the north side and as the Canadian
thistle(Cirsium arvense FACU) becomes prominent to t e south.
Sample point SP 1-1 Wet was taken from the north end i the wetland. The soils at sample point
SP1-1 Wet consisted of a silt loam at the surface beco ing a clay loam concentration matrix at
32 inches of depth. Hydric indicator Al2 (Thick Dark S rface) and F1 (Loamy Mucky Material)
were present. The soils at sample point SP1-1 Upl co sisted of layers of loam, turning more
sandy as depth increased.No hydric indicators were pre ent.
Sample point SP1-2 Wet was taken from the south by s uth west end of the wetland. The soils at
sample point SP1-2 Wet consisted of a silt loam at the s rface becoming a sandy loam depletion
matrix at 12 inches of depth. Hydric indicator S7 (Dark urface) was present. The soils at sample
point SP1-2 Upl consisted of layers of silt and sandy 1 am, turning to a loamy sandy as depth
increased. No hydric indicators were present.
Wetland hydrology was present at sample point P1-1 Wet with secondary indicators
Geomorphic Position(D2) and FAC-Neutral Test(DS). etland hydrology was present at sample
point SP1-1 Upl with secondary indicators Geomorph c Position (D2) and FAC-Neutral Test
(DS).
At sample point SP 1-2 Wet the secondary indicators D (Geomorphic Position) and DS (FAC-
Neutral Test) were present. At sample point SP1-2 pl there was no primary or secondary
indicators for wetland hydrology.
A third sample point was taken in the center of the etland just to the south of the semi-
permanently inundated pond on the east side of the p rcel. It appears that this area had been
affected by sidecasting of dredged soil as the ponded a ea looks to be an excavated offshoot of
the larger pond area to the east and off of the parcel. The vegetation here was dominated again by
reed canarygrass (Phalaris ar-undinacea FACV� as ell as common milkweed (Asclepias
Svoboda Ecological Resources 3 4245 Bayside Rd
Project Number: 2013-021-03 Orono,MN
syriaca FACU). The soils at sample point SP 1-3 consis ed of layers of silt loam becoming more
of a silt clay loam as depth increased. At sample p int SP 1-3 the secondary indicators D2
(Geomorphic Position) and DS (FAC-Neutral Test) wer present, indicating wetland hydrology.
Detailed soils, vegetation, and hydrology data for th delineated jurisdictional wetlands are
provided in the data sheets of the Technical Documents ection.
DISCUSSI
SER completed all on-site delineations based on the th ee required technical criteria as outlined
by the 1987 Manual: the presence of hydric soils, a redominance of hydrophytic vegetation,
and indicators of wetland hydrology in each basin. The site visit portion of the wetland
delineation was completed on 10/08/13.
SER personnel examined the subject property for are meeting jurisdictional wetland criteria
during the site visit and delineated the western, south and northern edges of the seasonally
inundated depression as being jurisdictional wetland, li ely a PEMC Type L (Figure 5). Detailed
soils, vegetation and hydrology data is provided in the data sheets of the Technical Documents
section.A set of figures is provided in the Figures sectio .
RECOMMENDA IONS
Activities that impact or could potentially impact we lands are regulated at several levels of
government. In Minnesota, the two primary jurisdicti ns are covered at the state and federal
levels by the provisions of the following legislative acti ns.
1* State jurisdiction by the Wetland Conservation A t of 1991 (WCA) administered by the
WCA Local Governmental Unit(LGU).
2* Federal jurisdiction by the Clean WaterAct of 1 72 and subsequent amendments.
Wetland protection is implemented by the Corps f Engineers (Corps)with permit
certification issued by the Environmental Protect on Agency.
While the wetland boundaries that SER has delineated re not official until approved by a WCA
approved local government unit (LGU), SER advises he property owner/developer to refrain
from any filling, draining, or excavating, or any im act to the area SER has delineated as
wetland. No grading or filling in wetland basins shoul commence until all necessary permits
have been obtained. Violation of wetland regulations m y result in substantial civil and criminal
penalties. Local ordinances may regulate wetland modi ications such as brush and tree removal
and burning in addition to grading and filling. Dependi g on the location of the property, buffers
around the wetland may also be protected. Any activiti s in the proximity of the wetland should
be cleared with appropriate WCA regulatory agencies. It is also advisable to have the wetland
boundary surveyed by a licensed land surveyor. Since t e pin flags used along the boundary can
be vandalized or inadvertently knocked over, a GP survey of the flags will assure the
permanence of the boundary. The client should also be ware that approved wetland boundaries
are typically valid for only three years from the date of proval.
Svoboda Ecological Resources 4 4245 Bayside Rd
Project Number. 2013-021-03 Orono,MN
To avoid project delays associated with wetland reg lations, it is essential that you acquire
necessary permits from all jurisdictional agencies befor initiating activities. A WCA Sequencing
form, a WCA and Army Corps of Engineers Replace ent Plan Application form, and a DNR
permit application are among the materials that you ay be required to submit if impacts are
proposed for the delineated wetlands. By initiating t e permit process as soon as possible,
potential costly delays to the project may be avoided.
Svoboda Ecological Resources $ 4245 Bayside Rd
Project Number: 2013-021-03 Orono,MN
i
CERTIFICAT ON
David Remucal completed the above-described deline ion on 9/20/2013. This delineation was
performed according to the procedures described by t e US Army Corps of Engineers in the
1987 Wetlands Delineation Manual and the 2007 Midwest Region Supplement Wetland
Delineation Manual. The delineation meets the stand rds and a criterion described in these
manuals and conforms to the applicable standards a d regulations in force at the time the
delineation was completed.
Report and graphics were prepared by David Remucal ( etland Ecologist) on this day
10/4/2013. The delineation report was reviewed by Fra Svoboda, President of Svoboda
Ecological Resources.
Client: CLIENT
Project Name:4245 Bayside Drive
Project No.: 2013-021-03
Location: Orono, MN
�"��-� �-a.e���.
GIS Technician
��,V� (�,�-�('.u,�,
Wetland Ecologist
c7i�e,�c�..-._ � .`
President, Svoboda Ecological Resources
10/8/13
Date
Svoboda Ecologicai Resources 6 4245 Bayside Rd
Project Number: 2013-021-03 Orono,MN
I
DATA SOUR ES
Minnesota Department of Natural Resources, Public Wa ers Inventory Basin Delineations,
Published 7/31/2008 and retrieved from http://deli.dnr.st te.mn.us
United States Fish and Wildlife Service National Wetla Inventory Map. Retrieved from
http://www.fws.gov/wetlands/Data/Mapper.html on 5/2 /12.
2010 Aerial Color Photos. Publicly Distributed by MN eo WMS Service.
Topographic maps obtained via the National Geographi Society's USA Topo service through
ESRI.
Web Soil Survey for Hennepin County, MN. Retrieved om
http://websoilsurvey.nres.usda.gov/app/HomePage.htm
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Svoboda Ecological Resources 7 4245 Bayside Rd
Project Number: 2013-021-03 Orono,MN
LITERATURE REF RENCED
Cowardin, L.M., V. Carter, F.C. Golet, and R.T. LaRoe. 979. Classification of Wetlands and
Deepwater Habitats of the United States. U.S. Fish and ildlife Service, FWS/OBS-79/31.
103pp.
Eggers, Steve D. and Donald M. Reed. 2011. Wetland P ants and Plant Communities of
Minnesota and Wisconsin, Third Edition. US Army Co s of Engineers, St. Paul District. 478pp,
unclassified.
Environmental Laboratory. 1987. 1987 U.S. Army C'orp of Engineers Wetlands Delineation
Manual. Technical Report Y-87-1, US Army Engineer aterways Experiment Station,
Vicksburg, Mississippi.
Gleason, H.A. and A.C. Cronquist. 1991.Manual of Vas ular Plants of Northeastern United
States and Adjacent Canada. New York Botanical Gard , Bronx. 910pp.
Lichvar, R.W. 2013. The National Wetland Plant L,ist: 013 wetland ratings. Phytoneuron
2013-49: 1-241. htt ://i-s«isias.ci-i-el.usace.arn� .�nil/NW L/
Shaw, S.P., and C.G. Fredine. 1956. Wetlands of the Uni d States. U.S. Fish and Wildlife
Service, Circular 39. 67pp.
U.S.Army Corps of Engineers.August 2010. Regional upplement to the Corps of Engineers
Wetland Delineation Manual: Midwest Region (Versio 2.0). ERDC/EL TR-10-16. Vicksburg,
MS: US Army Engineer Research and Development Ce ter.
Svoboda Ecological Resources , g 4245 Bayside Rd
ProjectNumber: 2013-021-03 Orono,MN
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FIGURES
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Overlaid on 2012 Aerial Photo
,'�SVQ BC�DA 20�3-020
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`� E�o9ogica! R�saurces Feet 4245 Bayside Rd
Orono, MN
THE TECHNICAL DOCUME TATION SECTION
Field Data Sheet
WETLAND DETERMINATION DATA FORM-Midwest egion
ProjecUSite Lake Lot Adjacent to 4245 Bayside City/County: Orono/Hennepin Sampling Date: 10/8/2013
ApplicanUOwner: VCI Capital State: MN ampling Point: SP 1 1 Upl
Investigator(s): FS,TK �ection,Township,Range: SO6 T117N R23W
Landform(hillslope,terrace,etc.): Depression Local relief(concave,conve ,none): concave
Slope(%): 0 Lat: Long: Datum: NAD83
Soil Map Unit Name Klossner soils,depressional JWI Classificat n: PEMC
Are climatic/hydrologic conditions of the site typical for this time of the year? Y (If np,expl in in remarks)
Are vegetation ,soil ,or hydrology significantly disturbed? re"normal circumstances"
Are vegetation ,soil ,or hydrology naturally problematic? present? Yes
SUMMARY OF FINDINGS (If need d,explain any answers in remarks.)
Hydrophytic vegetation present? Y
Hydric soil present? N Is the sampled area within wetland? N
Indicators of wetland hydrology present? Y `yes,optional wetland site ID:
Remarks:(Explain alternative procedures here or in a separate report.)
VEGETATION--Use scientific names of plants.
Absolute Dominan Indicator pomin nce Test Worksheet
Tree Stratum (Plot size: 30 ) %Cover t Species Staus Number of Dominant Species
1 that are BL,FACW,or FAC: 2 (A)
2 Total Number of Dominant
3 Spe es Across all Strata: 2 (B)
4 Percent f Dominant Species
5 that are BL,FACW,or FAC: 100.00% (A/B)
0 =Total Cover
S�a ling/Shrub stratun (Plot size: 15' ) Preval ce Index Worksheet
1 Total%Cover of:
2 OBL sp cies 0 x 1= 0
3 FACW ecies 48 x 2= 96
4 FAC sp cies 48 x 3= 144
5 FACU s ecies 0 x 4= 0
0 =Total Cover UPL sp cies 0 x 5= 0
Herb stratum (Plot size: 5' ) Column totals 96 (A) 240 (B)
1 Phalaris arundinacea 48 Y FACW Prevale ce Index=B/A= 2.50
2 Poa prafensis 48 Y FAC
3 Alliaria petiolata 2 N FAC Hydrop ytic Vegetation Indicators:
4 Ra d test for hydrophytic vegetation
5 X Do inance test is>50°/o
6 X Pre alence index is<_3.0*
� Mor hogical adaptations`(provide
8 sup orting data in Remarks or on a
g sep rate sheet)
10 Pro lematic hydrophytic vegetation*
98 =Total Cover (ex lain)
WOOdv vine StfBtUm (Plot SiZ@: 30� ) •Indicato of hydric soil and wetland hydrology must be
� p sent,unless disturbed or problematic
2 y op ic
0 =Total Cover �eg tation
pre ent? Y
Remarks:(Include photo numbers here or on a separate sheet)
US Amy Corps of Engineers Midwest Region
II
SOIL Sampling Point: SP 1 1 Upl
Profile Description: (Describe to the depth needed to document the indicator or confirm the bsence of indicators.)
Depth Matrix Redox Features
(Inches) Color(moist) % Color(moist) % Type' Loc" Texture Remarks
12 5YR 2.5/1 100 Silt Loam
22 10YR 2/1 100 Silt Loam Compacted
32 10YR 2/2 100 Sandy Loam
"Type:C=Concentration,D=Depletion,RM=Reduced Matrix,MS=Masked Sand Grains. "' ocation:PL=Pore Lining,M=Matrix
Hydric Soil Indicators: Indicators for roblematic Hydric Soils:
Histisol(A1) Sandy Gleyed Matrix(S4) Coast Prai Redox(A16)(LRR K,L,R)
Histic Epipedon(A2) Sandy Redox(S5) Dark Surfa (S7)(LRR K,L)
Black Histic(A3) Stripped Matrix(S6) 5 cm Muck Peat or Peat(S3)(LRR K,L,R)
Hydrogen Sulfide(A4) Loamy Mucky Mineral(F1) Iron-Manga ese Masses(F12)(LRR K,L,R)
Stratified Layers(A5) Loamy Gleyed Matrix(F2) Very Shallo Dark Surface(TF12)
2 cm Muck(A10) Depleted Matrix(F3) Other(expl in in remarks)
Depleted Below Dark Surface(A11) Redox Dark Surface(F6)
Thick Dark Surface(Al2) Depleted Dark Surface(F7) 'Indicators of hydrophytic vegetation and weltand
Sandy Mucky Mineral(S1) Redox Depressions(F8) hydrodogy m st be present,unless disturbed or
problematic
Restrictive Layer(if observed):
Type: Hydric soil pr sent? N
Depth(inches):
Remarks:
Highly compacted at 20"depth
HYDROLOGY
Wetland Hydrology Indicators:
Primary Indicators(minimum of one is reauired:check all that aoolvl Seconda In ic tors minim m of two re uired
Surface Water(A1) Aquatic Fauna(813) Su ace Soil Cracks(B6)
High Water Table(A2) True Aquatic Plants(B14) Dra age Patterns(810)
Saturation(A3) Hydrogen Sulfide Odor(C1) Dry Season Water Table(C2)
Water Marks(61) Oxidized Rhizospheres on Living Roots�Cra ish Burrows(C8)
Sediment Deposits(B2) (C3) �Sat ration Visible on Aerial Imagery(C9)
Drift Deposits(83) Presence of Reduced Iron(C4) Stu ted or Stressed Plants(D1)
Algal Mat or Crust(B4) Recent Iron Reduction in Tilled Soils �Ge morphic Position(D2)
Iron Deposits(BS) (C6) �C FA Neutral Test(D5)
Inundation vsible on Aerial Imagery(B7) Thin Muck Surface(C7) �
Sparsely Vegetated Concave Surface(88) Gauge or Well Data(D9)
Water-Stained Leaves(B9) O[her(Explain in Remarks)
Field Observations:
Surface water present? Yes No X Depth(inches):
Water table present? Yes No X Depth(inches): Indicators of wetland
Saturation present? Yes No X Depth(inches): hydrology present? Y
(includes capillary fringe)
Describe recorded data(stream gauge,monitoring well,aerial photos,previous inspections),if availa le:
Remarks:
US Army Corps of Engineers Midwest Region
;
WETLAND DETERMINATION DATA FORM-Midwest egion
ProjecUSite Lake Lot Adjacent to 4245 Bayside City/County: Orono ampling Date: 10/8/2013
ApplicanUOwner: VCI Capital State: MN ampling Point: SP 1_1 Wet
Investigator(s): FS,TK �ection,Township,Range: S06 T117N R23W
Landform(hilislope,terrace,etc.): Depression Local relief(concave,convex none): concave
Slope(%): 0 Lat: Long: atum: NAD83
Soil Map Unit Name Klossner soils,depressional JWI Classificati n: PEMC
Are climatic/hydrologic conditions of the site typical for this time of the year? Y (If no,expl in in remarks)
Are vegetation ,soil ,or hydrology significantly disturbed? re"normal circumstances"
Are vegetation ,soil ,or hydrology naturally problematic? present? Yes
SUMMARY OF FINDINGS (If need d,explain any answers in remarks.)
Hydrophytic vegetation present? Y
Hydric soil present? Y Is the sampled area within wetland? Y
Indicators of wetland hydrology present? Y `yes,optional wetland site ID:
Remarks:(Explain alternative procedures here or in a separate report.)
VEGETATION--Use scientific names of plants.
Absolute Dominan Indicator pomin nce Test Worksheet
Tree Stratum (Plot size: 30' ) %Cover t Species Staus Number f Dominant Species
� that are BL,FACW,or FAC: 1 (A)
2 Total Number of Dominant
3 Spe es Across all Strata: 1 (B)
4 Percent f Dominant Species
5 that are BL,FACW,or FAC: 100.00% (A/B)
0 =Total Cover
Sa�lina/Shrub stratun (Plot size: 15' ) Preval ce Index Worksheet
� Total°/Cover of:
2 OBL sp cies 0 x 1= 0
3 FACW pecies 99 x 2= 198
q FAC sp cies 0 x 3= 0
5 FACU ecies 1 x 4= 4
0 =Total Cover UPL sp cies 0 x 5= 0
Herb stratum (Plot size: 5' ) Column totals 100 (A) 202 (B)
1 Phalaris arundinacea 98 Y FACW Prevale ce Index=B/A= 2.02
2 Urtica dioica 1 N FACW
3 Cirsium arvense 1 N FACU Hydro ytic Vegetation Indicators:
q Ra 'd test for hydrophytic vegetation
5 X Do inance test is>50%
g X Pre alence index is 53.0'
7 Mo hogical adaptations'(provide
g sup orting data in Remarks or on a
g sep rate sheet)
�p Pro lematic hydrophytic vegetation"
100 =Total Cover (ex lain)
Woodv vine stratum (Plot SiZO: 30� ) •Indicato of hydric soil and wetland hydrology must be
� esent,unless disturbed or problematic
2 y rop ytic
0 =Total Cover �e tation
pre ent? Y
Remarks:(Include photo numbers here or on a separate sheet)
I
US Amy Corps of Engineers Midwest Region
SOIL Sampling Point: SP 1 1 Wet
Profile Description: (Describe to the depth needed to document the indicator or confirm the bsence of indicators.)
Depth Matrix Redox Features
(Inches) Color(moist) % Color(moist) % Type' Loc" Texture Remarks
16 10YR 2/2 100 Silt Loam
32 7.5YR 2.5/1 100 Mucky Silt Loam
40 7.5YR 2.5/1 90 10YR 4/4 10 C M Clay Loam
`Type:C=Concentration,D=Depletion,RM=Reduced Matrix,MS=Masked Sand Grains. " ocation:PL=Pore Lining,M=Matrix
Hydric Soil Indicators: Indicators for roblematic Hydric Soils:
Histisol(A1) Sandy Gleyed Matrix(S4) Coast Prai Redox(A16)(LRR K,L,R)
Histic Epipedon(A2) Sandy Redox(SS) Dark Surfa e(S7)(LRR K,L)
Black Histic(A3) Stripped Matrix(S6) 5 cm Muck Peat or Peat(S3)(LRR K,L,R)
Hydrogen Sulfide(A4) X Loamy Mucky Mineral(F1) Iron-Manga ese Masses(F12)(LRR K,L,R)
Stratified Layers(A5) Loamy Gleyed Matrix(F2) Very Shall Dark Surface(TF12)
2 cm Muck(A10) Depleted Matrix(F3) Other(expl in in remarks)
Depleted Below Dark Surface(A11) Redox Dark Surface(F6)
X Thick Dark Surface(Al2) Depleted Dark Surface(F7) `Indicators o hydrophytic vegetation and weltand
Sandy Mucky Mineral(S1) Redox Depressions(F8) hydrology st be present,unless disturbed or
problematic
Restrictive Layer(if observed):
Type: Hydric soil p sent? Y
Depth(inches):
Remarks:
HYDROLOGY
Wetland Hydrology Indicators:
Primary Indicators(minimum of one is reauired:check all that aoolvl Se ond Indicators minim m f two re ir
Surface Water(A1) Aquatic Fauna(613) Su face Soil Cracks(86)
High Water Table(A2) True Aquatic Plants(614) '—Dr inage Pattems(B10)
Saturation(A3) Hydrogen Sulfide Odor(C1) D -Season Water Table(C2)
Water Marks(B1) Oxidized Rhizospheres on Living Roots Cr yfish Burrows(CS)
Sediment Deposits(B2) (C3) Sa ration Visible on Aerial Imagery(C9)
Drift Deposits(B3) Presence of Reduced Iron(C4) St nted or Stressed Plants(D1)
Algal Mat or Crust(64) Recent Iron Reduction in Tilled Soils X G morphic Position(D2)
Iron Deposits(B5) (C6) X F -Neutral Test(D5)
Inundation Visible on Aerial Imagery(67) Thin Muck Surface(C7)
Sparsely Vegetated Concave Surface(88) Gauge or Well Data(D9)
Water-Stained Leaves(B9) Other(Explain in Remarks)
Field bservations:
Surface water present? Yes No X Depth(inches):
Water table present? Yes No X Depth(inches): Indicators of wetland
Saturation present? Yes No X Depth(inches): hydrology present? Y
(includes capillary fringe)
Describe recorded data(stream gauge,monitoring well,aerial photos,previous inspections),if avail ble:
Remarks:
i
US Army Corps of Engineers Midwest Region
WETLAND DETERMINATION DATA FORM-Midwest egion
ProjecVSite Lake Lot Adjacent to 4245 Bayside City/County: Orono ampling Date: 10/8/2013
ApplicanUOwner: VCI Capital State: MN ampling Point: SP 1 2 Upl
Investigator(s): FS,TK �ection,Township,Range: SO6 T117N R23W
Landform(hillslope,terrace,etc.): Depression Local relief(concave,conve none): concave
Slope(%): 0 Lat: Long: Datum: NAD83
Soil Map Unit NameAngus-Kilkenny complex,2-6 percent slopes JWI Classificati n: None
Are climatic/hydrologic conditions of the site typical for this time of the year? Y (If no,expl in in remarks)
Are vegetation ,soil ,or hydrology significantly disturbed? re"normal circumstances"
Are vegetation ,soil ,or hydrology naturally problematic? present? Yes
SUMMARY OF FINDINGS (If need d,explain any answers in remarks.)
Hydrophytic vegetation present? N
Hydric soil present? N Is the sampled area within wetland? N
Indicators of wetland hydrology present? N `yes,optional wetland site ID:
Remarks:(Explain alternative procedures here or in a separate report.)
VEGETATION--Use scientific names of plants.
Absolute Dominan Indicator pomin nce Test Worksheet
Tree Stratum (Plot size: 30' ) %Cover t Species Staus Number f Dominant Species
1 that are BL,FACW,or FAC: 1 (A)
2 Total umber of Dominant
3 Spec s Across all Strata: 2 (B)
4 Percent f Dominant Species
5 that are BL,FACW,or FAC: 50.00% (A/B)
0 =Total Cover
Saplina/Shrub stratun (Plot size: 15' ) Prevale ce Index Worksheet
1 Total% over of:
2 OBL sp cies 0 x 1= 0
3 FACW ecies 41 x 2= 82
4 FAC sp cies 0 x 3= 0
5 FACU s ecies 45 x 4= 180
0 =Total Cover UPL sp ies 5 x 5= 25
Herb stratum (Plot size: 5' ) Column otals 91 (A) 287 (B)
1 Cirsium arvense 45 Y FACU Prevale ce Index=B/A= 3.15
2 Phalaris arundinacea 40 Y FACW
3 Verbascum thapsus 5 N UPL Hydrop ytic Vegetation Indicators:
4 Rap d test for hydrophytic vegetation
5 �Do inance test is>50%
6 Pre alence index is s3.0`
� �Mor hogical adaptations'(provide
8 sup orting data in Remarks or on a
9 sep rate sheet)
10 Pro ematic hydrophytic vegetation"
90 =Total Cover (ex ain)
Woody vine stratum (Plot size: 30' ) •indicaior of hydric soil and wetland hydrology must be
1 Vitis riparia 1 N FACW p sent,unless dismrbed or problematic
y y op y�c
1 =Total Cover �eg tation
pre ent? N
Remarks:(Include photo numbers here or on a separate sheet)
US Amy Corps of Engineers Midwest Region
SOIL Sampling Point: SP 1_2 Upl
Profile Description: (Describe to the depth needed to document the indicator or confirm the bsence of indicators.)
Depth Matrix Redox Features
(Inches) Color(moist) % Color(moist) % Type' Loc" Texture Remarks
8 10YR 3/1 100 Silt Loam
20 10YR 4/2 100 Sandy Loam
25 10YR 4/3 100 Loamy Sand
'Type:C=Concentration,D=Depletion,RM=Reduced Matrix,MS=Masked Sand Grains. "* ocation:PL=Pore Lining,M=Matrix
Hydric Soil Indicators: Indicators for oblematic Hydric Soils:
Histisol(A1) Sandy Gleyed Matrix(S4) Coast Prairi Redox(A16)(LRR K,L,R)
Histic Epipedon(A2) Sandy Redox(S5) Dark Surfac (S7)(LRR K,L)
Black Histic(A3) Stripped Matrix(S6) 5 cm Muck Peat or Peat(S3)(LRR K,L,R)
Hydrogen Sulfide(A4) Loamy Mucky Mineral(F1) Iron-Manga ese Masses(F12)(LRR K,L,R)
Stratifed Layers(A5) Loamy Gleyed Matrix(F2) Very Shallo Dark Surface(TF12)
2 cm Muck(A10) Depleted Matrix(F3) Other(expl in in remarks)
Depleted Below Dark Surface(A11) Redox Dark Surface(F6)
Thick Dark Surface(Al2) Depleted Dark Surface(F7) 'Indicators of hydrophytic vegetation and weltand
Sandy Mucky Mineral(S1) Redox Depressions(F8) hydrology m st be present,unless disturbed or
problematic
Restrictive Layer(if observed):
Type: Hydric soil pr sent? N
Depth(inches):
Remarks:
HYDROLOGY
Wetland Hydrology Indicators:
Primarv Indicators(minimum of one is reauired:check all that a�olv) e onda Indi a rs�minimum of two reauired)
Surface Water(A1) Aquatic Fauna(813) Su ace Soil Cracks(86)
High Water Table(A2) True Aquatic Plants(B14) �Dra age Pattems(610)
Saturation(A3) Hydrogen Sulfide Odor(C1) �Dry eason Water Table(C2)
Water Marks(61) Oxidized Rhizospheres on Living Roots�Cra ish Burrows(C8)
Sediment Deposits(82) (C3) �Sat ration Visible on Aerial Imagery(C9)
Drik Deposits(B3) Presence of Reduced Iron(C4) Stu ted or Stressed Plants(Dt)
Algal Mat or Crus[(64) Recent Iron Reduction in Tilled Soils Ge morphic Position(D2)
Iron Deposits(B5) (C6) FA -Neutral Test(D5)
Inundation Visible on Aerial Imagery(B7) Thin Muck Surface(C7)
Sparsely Vegetated Concave Surface(88) Gauge or Well Data(D9)
Water-Stained Leaves(B9) Other(Explain in Remarks)
Field Observations:
Surface water present? Yes No X Depth(inches):
Water table present? Yes No X Depth(inches): Indicators of wetland
Saturation present? Yes No X Depth(inches): hydrology present? N
(includes capillary fringe)
Describe recorded data(stream gauge,monitoring well,aerial photos,previous inspections),if avail le:
Remarks:
US Army Corps of Engineers Midwest Region
WETLAND DETERMINATION DATA FORM-Midwest egion
ProjecUSite Lake Lot Adjacent to 4245 Bayside City/Counry: Orono Sampling Date: 10/8/2013
ApplicanUOwner: VCI Capital State: MN ampling Point: SP 1_2 Wet
Investigator(s): FS,TK >ection,Township,Range: SO6 T117N R23W
Landform(hillslope,terrace,etc.): Depression Local relief(concave,conve ,none): concave
Slope(%): 0 Lat: Long: Datum: NAD83
Soil Map Unit NameKlossner soils,depressional JWI Classificat' n: PEMC
Are climatic/hydrologic conditions of the site typical for this time of the year? Y (If no,expl in in remarks)
Are vegetation ,soil ,or hydrology significantly disturbed? re"normal circumstances"
Are vegetation ,soil ,or hydrology naturally problematic? present? Yes
SUMMARY OF FINDINGS (If need d,explain any answers in remarks.)
Hydrophytic vegetation present? Y
Hydric soil present? Y Is the sampled area within wetland? Y
Indicators of wetland hydrology present? Y `yes,optional wetland site ID:
Remarks:(Explain alternative procedures here or in a separate report.)
VEGETATION--Use scientific names of plants.
Absolute Dominan Indicator pomin nce Test Worksheet
Tree Stratum (Plot size: 30' ) %Cover t Species Staus Number f Dominant Species
1 that are BL,FACW,or FAC: 1 (A)
2 Total Number of Dominant
3 Spe es Across all Strata: 1 (B)
4 Percent f Dominant Species
5 that are BL,FACW,or FAC: 100.00% (A/B)
0 =Total Cover
Saolino/Shrub stratun (Plot size: 15' ) Preval ce Index Worksheet
1 Total% over of:
2 OBL sp cies 0 x 1= 0
3 FACW ecies 99 x 2= 198
4 FAC sp cies 0 x 3= 0
5 FACU s ecies 1 x 4= 4
0 =Total Cover UPL sp ies 0 x 5= 0
Herb stratum (Plot size: 5' ) Column totals 100 (A) 202 (B)
1 Phalaris arundinacea 99 Y FACW Prevale ce Index=B/A= 2.02
2 Cirsium arvense 1 N FACU
3 Hydrop ytic Vegetation Indicators:
4 Ra d test for hydrophytic vegetation
5 X Do inance test is>50%
6 X Pre alence index is s3.0'
� Mor hogical adaptations"(provide
8 sup orting data in Remarks or on a
g sep rate sheet)
10 Pro lematic hydrophytic vegetation'
100 =Total Cover (ex ain)
WOOdV Vin@ StfBtUm (Plot SiZ@: 30' ) `Indicator of hydric soil and wetland hydrology must be
1 p sent,unless disturbed or problematic
2 y op iC
0 =Total Cover �eg tation
pre ent? Y
Remarks:(Include photo numbers here or on a separate sheet)
US Amy Corps of Engineers Midwest Region
SOIL Sampling Point: SP 1 2 Wet
Profile Description: (Describe to the depth needed to document the indicator or confirm the bsence of indicators.)
Depth Matrix Redox Features
(Inches) Color(moist) % Color(moist) % Type' Loc" Texture Remarks
12 10YR 2/1 100 Silt Loam Organic Matter Present
25 10YR 3/2 85 10YR 5/1 15 D M Sandy Loam
`Type:C=Concentration,D=Depletion,RM=Reduced Matrix,MS=Masked Sand Grains. " ocation:PL=Pore Lining,M=Matrix
Hydric Soil Indicators: Indicators for roblematic Hydric Soils:
Histisol(A1) Sandy Gleyed Matrix(S4) Coast Prairi Redox(A16)(LRR K,L,R)
Histic Epipedon(A2) Sandy Redox(S5) X Dark Surfa (S7)(LRR K,L)
Black Histic(A3) Stripped Matrix(S6) 5 cm Muck Peat or Peat(S3)(LRR K,L,R)
Hydrogen Sulfide(A4) Loamy Mucky Mineral(F1) Iron-Manga ese Masses(F12)(LRR K,L,R)
Stratifed Layers(A5) Loamy Gleyed Matrix(F2) Very Shallo Dark Surface(TF12)
2 cm Muck(A10) Depleted Matrix(F3) _Other(expl in in remarks)
Depleted Below Dark Surface(A11) Redox Dark Surface(F6)
Thick Dark Surface(Al2) Depleted Dark Surface(F7) `Indicators of hydrophytic vegetation and weltand
Sandy Mucky Mineral(S1) Redox Depressions(F8) hydrology m st be present,unless disturbed or
— problematic
Restrictive Layer(if observed):
Type: Hydric soil pr sent? Y
Depth(inches):
Remarks:
HYDROLOGY
Wetland Hydrology Indicators:
Primarv Indicators(minimum of one is reauired'check all that aoolvl e n a In i t r minimum f two r uire
Surface Water(A1) Aquatic Fauna(B13) Su ece Soil Cracks(B6)
High Water Table(A2) True Aquatic Plants(814) Dra age Pattems(B10)
Saturation(A3) Hydrogen Sulfide Odor(Ct) Dry eason Water Table(C2)
Water Marks(81) Oxidized Rhizospheres on Living Roots Cra sh Burrows(C8)
Sediment Deposits(B2) (C3) Sat ration Visible on Aerial Imagery(C9)
Drift Deposi[s(B3) Presence of Reduced Iron(C4) Stu ted or Stressed Plants(D1)
Algal Mat or Crust(84) Recent Iron Reduction in Tilled Soils X Ge morphic Position(D2)
Iron Deposits(B5) (C6) X FA -Neu[ral Test(D5)
Inundation Visible on Aerial Imagery(B7) Thin Muck Surface(C7) ^
Sparsely Vegetated Concave Surface(B8) Gauge or Well Data(D9)
Water-Stained Leaves(89) Other(Explain in Remarks)
Field Observations:
Surface water present? Yes No X Depth(inches):
Water table present? Yes No X Depth(inches): Indicators of wetland
Saturation present? Yes No X Depth(inches): hydrology present? Y
(includes capillary fringe)
Describe recorded data(stream gauge,monitoring well,aerial photos,previous inspections),if avail le:
Remarks:
US Army Corps of Engineers Midwest Region
WETLAND DETERMINATION DATA FORM-Midwest egion
ProjecUSite Lake Lot Adjacent to 4245 Bayside City/County: Orono ampling Date: 10/8/2013
ApplicanUOwner: VCI Capital State: MN ampling Point: SP 1 3
Investigator(s): FS,TK �ection,Township,Range: S06 T117N R23W
Landform(hillslope,terrace,etc.): Depression Local relief(concave,conve none): concave
Slope(%): 0 Lat: Long: Datum: NAD83
Soil Map Unit NameKlossner soils,depressional JWI Classificati n: PEMC
Are climatic/hydrologic conditions of the site typical for this time of the year? Y (If no,expl in in remarks)
Are vegetation ,soil ,or hydrology significantly disturbed? re"normal circumstances"
Are vegetation ,soil ,or hydrology naturally problematic? present? Yes
SUMMARY OF FINDINGS (If need d,explain any answers in remarks.)
Hydrophytic vegetation present? Y
Hydric soil present? N Is the sampled area within wetland? N
Indicators of wetland hydrology present? Y `yes,optional wetland site ID:
Remarks:(Explain alternative procedures here or in a separate report.)
VEGETATION--Use scientific names of plants.
Absolute Dominan Indicator pomin ce Test Worksheet
Tree Stratum (Plot size: 30' ) %Cover t Species Staus Number f Dominant Species
� that are BL,FACW,or FAC: 1 (A)
2 Total Number of Dominant
3 Spe es Across all Strata: 1 (B)
4 Percent f Dominant Species
5 that are BL,FACW,or FAC: 100.00% (A/B)
0 =Total Cover
Saolino/Shrub straturr (Plot size: 15' ) Preval ce Index Worksheet
� Total%Cover of:
z OBL sp cies 0 x 1= 0
3 FACW ecies 95 x 2= 190
q FAC sp cies 0 x 3= 0
5 FACU s ecies 17 x 4= 68
0 =Total Cover UPL sp cies 0 x 5= 0
Herb stratum (Plot size: 5' ) Column totals 112 (A) 258 (B)
1 Phalaris arundinacea 95 Y FACW Prevale ce Index=BIA= 2.30
2 Asclepias syriaca 15 N FACU
3 Cirsium arvense 2 N FACU Hydrop ytic Vegetation Indicators:
q Ra d test for hydrophytic vegetation
5 X Do inance test is>50%
g X Pre alence index is<_3.0'
7 Mor hogical adaptations`(provide
8 sup orting data in Remarks or on a
g sep rate sheet)
10 Pro lematic hydrophytic vegetation'
112 =Tota�Cover (ex lain)
Woody vine stratum (PIOt SiZO: 30� ) 'Indicato of hydric soil and wetland hydrology must be
� p sent,unless disturbed or problematic
2 y op ytic
0 =Total Cover �eg tation
pre ent? Y
Remarks:(Include photo numbers here or on a separate sheet)
US Amy Corps of Engineers Midwest Region
SOIL Sampling Point: SP 1 3
Profile Description: (Describe to the depth needed to document the indicator or confirm the bsence of indicators.)
Depth Matrix Redox Features
(Inches) Color(moist) % Color(moist) % Type' Loc" Texture Remarks
10 10YR 2/1 100 Silt Loam
25 10YR 3/4 90 7.5YR 5/6 10 C PL/M Silty clay Loam
`Type:C=Concentration,D=Depletion,RM=Reduced Matrix,MS=Masked Sand Grains. " ocation:PL=Pore Lining,M=Matrix
Hydric Soil Indicators: Indicators for roblematic Hydric Soils:
Histisol(A1) Sandy Gleyed Matrix(S4) Coast Prair Redox(A16)(LRR K,L,R)
Histic Epipedon(A2) Sandy Redox(S5) Dark Surfa (S7)(LRR K,L)
Black Histic(A3) Stripped Matrix(S6) 5 cm Muck Peat or Peat(S3)(LRR K,L,R)
Hydrogen Sulfide(A4) Loamy Mucky Mineral(F1) Iron-Manga ese Masses(F12)(LRR K,L,R)
Stratified Layers(A5) Loamy Gleyed Matrix(F2) Very Shallo Dark Surface(TF12)
2 cm Muck(A10) Depleted Matrix(F3) Other(expl in in remarks)
Depleted Below Dark Surface(A11) Redox Dark Surface(F6)
Thick Dark Surface(Al2) Depleted Dark Surface(F7) 'Indicators o hydrophytic vegetation and weltand
Sandy Mucky Mineral(S1) Redox Depressions(F8) hydrology m st be present,unless disturbed or
— problematic
Restrictive Layer(if observed):
Type: Hydric soil p sent? N
Depth(inches):
Remarks:
Site could have soil from side cast from digging out a small pond
HYDROLOGY
Wetland Hydrology Indicators:
Primary Indicators(minimum of one is reauired:check all that aoolvl Se ond Indicator minimum of two re uired
Surface Water(A1) Aquatic Fauna(B13) Su face Soil Cracks(86)
High Water Table(A2) True Aquatic Plants(614) Dr inage Pattems(610)
Saturation(A3) Hydrogen Sulfide Odor(C1) iDr-Season Water Table(C2)
Water Marks(61) Oxidized Rhizospheres on Living Roots Cr yfish Burcows(C8)
Sediment Deposits(B2) (C3) Sa uration Visible on Aerial Imagery(C9)
Drift Deposits(83) Presence of Reduced Iron(C4) St nted or Stressed Plants(D1)
Algal Mat or Crust(B4) Recent Iron Reduction in Tilled Soils X Ge morphic Position(D2)
Iron Deposits(B5) (C6) X FA -Neutral Test(D5)
Inundation Visible on Aerial Imagery(B7) Thin Muck Surface(C7) i
Sparsely Vegetated Concave Surface(BS) Gauge or Well Data(D9)
Water-Stained Leaves(B9) �Other(Explain in Remarks)
ield bservations:
Surface water present? Yes No X Depth(inches):
Water table present? Yes No X Depth(inches): Indicators of wetland
Saturation present? Yes No X Depth(inches): hydrology present? Y
(includes capillary fringe)
Describe recorded data(stream gauge,monitoring well,aerial photos,previous inspections),if avail ble:
Remarks:
US Army Corps of Engineers Midwest Region
�I
THE TECHNICAL DOCUMEN ATION SECTION
Plant Indicatar Sta s
INDICATOR CATE ORIES*
�
Obligate Wetland (OBL)—Occur almost always (esti ated probability>99%) under natural
conditions in wetlands.
Facultative Wetland (FACW)—Usually occur in wetl nds (estimated probabiliry 67%- 99%),
but occasionally found in non-wetlands.
Facultative(FAC)—Equally likely to occur in wetland or non-wetlands (estimated probability
34% - 66%).
Facultative Upland (FACU)—Usually occur in non-w tlands (estimated probability 67%-
99%), but occasionally found in wetlands (estimated pr bability l%-33%).
Obligate Upland (UPL)—Occur in wetlands in another region, but occur almost always
(estimated probability>99%) under natural conditions i non-wetlands in the region specified. If
a species does not occur in wetlands in any region, it is ot on the National List.
*Reed, P.B. 1988. National list of plant species that oc ur in wetlands: Minnesota. National
Wetlands Inventory, U.S. Fish and Wildlife Service, St. etersburg, Florida.
THE TECHNICAL DOCUMEN ATION SECTION
Soil Series Descript' ns
Acquired from Natural Resource Conservation Service ebsite, Official Soil Series Descriptions
ANGUS SERIES
The Angus series consists of very deep,well drained soils for d in calcareous loamy glacial till on
moraines and till plains.Permeability is moderate. Slopes rang from 2 to 5 percent.Mean annual
precipitation is about 28 inches.Mean annual air temperature i about 46 degrees F.
TAXONOMIC CLASS: Fine-loamy, mixed, super ctive, mesic Mollic Hapludalfs
TYPICAL PEDON: Angus loam with a convex slo e of about 5 percent on a ground
moraine in a cultivated field. (Colors are for moist s il unless otherwise noted.)
Ap--O to 8 inches; black (lOYR 2/1) loam, dark gra sh brown(lOYR 4/2) dry; weak fine
granular structure; friable; many very fine roots; abo t 2 percent gravel; neutral; abrupt
smooth boundary. (6 to 10 inches thick)
Btl--8 to 23 inches; dark yellowish brown (lOYR 4/ ) clay loam; moderate medium
angular blocky structure; firm; common faint brown lOYR 4/3) clay films on ped
interiors; many very fine roots; about 3 percent grav 1; slightly acid; gradual wavy
boundary.
Bt2--23 to 35 inches; brown(lOYR 4/3) clay loam; oderate medium subangular blocky
structure; firm; common faint very dark grayish bro n(lOYR 3/2) clay films on faces of
peds and root channels; common very fine roots; ab ut 5 percent gravel; slightly acid;
clear wavy boundary. (Combined thickness of the Bt horizons is 15 to 40 inches)
BC--35 to 40 inches; brown(lOYR 5/3) clay loam; eak medium subangular blocky
structure; friable; few faint brown(lOYR 4/3) clay f ms in root channels; about 4 percent
gravel; slightly effervescent; slightly alkaline; gradu 1 wavy boundary. (0 to 12 inches
thick)
C--40 to 80 inches; brown (l 0YR 5/3) loam; massiv ; friable; common fine distinct
grayish brown(2.SY 5/2) Fe depletion and common edium distinct yellowish brown
(lOYR 5/6) Fe concentrations; about 7 percent grave ; strongly effervescent; slightly
alkaline.
TYPE LOCATION: Wright County, Minnesota; ab ut 1 mile south of Montrose, 200
feet north and 80 feet east of the southwest corner o sec. 1, T. 118 N., R. 26 W.; USGS
Waverly quadrangle; lat. 45 degrees 03 minutes 20 s conds N.; long. 93 degrees 54
minutes 38 seconds W., NAD27.
RANGE IN CHARACTERISTICS: Depth to free alcium carbonates ranges from 24
to 54 inches. Rock fragments of mixed lithology co prise 2 to 8 percent of the volume
throughout. Soil saturation occurs in the lower third i the series control section for
periods of one month or more. These soils are dry fo more than 60 days in the soil
moisture control section during the 120 days followi g the summer solstice. The clay
content ranges from 22 to 30 percent and the sand co tent ranges from 30 to 45 percent
throughout.
The A or Ap horizon has hue of lOYR, value of 2 or 3 and chroma of 1 to 3. It is
typically loam or clay loam,but silt loam, sandy loa and fine sandy loam are within the
range. The reaction is moderately acid to neutral.
Some pedons have a E horizon with hue of l OYR, v lue of 4 or 5, and chroma of 1 to 3.
It is loam, sandy loam or fine sandy loam. The reacti n is moderately acid to neutral.
The Bt horizon has hue of lOYR or 2.SY, value of 4 r 5, and chroma of 3 or 4. It is clay
loam, loam, or sandy clay loam. Redoximorphic fea res are present in the lower part of
the Bt horizon in some pedons. The B/A clay ratios nge from 1.2 to 1.4 . It is strongly
acid to slightly acid in the upper part and moderatel acid to neutral in the lower part.
A Bk horizon is present in some pedons.
The BC horizon has soil color and textures similar t the Bt and C horizon respectively.
Clay films are on ped faces or root channels. The rea tion is slightly acid to slightly
alkaline.
The C horizon has hue of 2.SY or lOYR, value of 4 t 6 and chroma of 3 to 5. It is loam
or clay loam. It is slightly alkaline or moderately alk line. Redox depletions with chroma
of 2 or less are in this horizon.
COMPETING SERIES: These are the Ar�,yle, Bal imoi-e, Bassett, Bloomin�, Caleb,
Dowagiac, Dunbrid��e, Gara, Koi�onis, Laui•amie, Le.ter, Longlois, Lydick, Mohawk,
Neda,Newcoiner, Oneco, Orwood, Racinc, Raroi�t, ebbo, Tao�i, Waucoma, and
Winnesluek soils. The Argyle, Baltimore, Blooming, Gara Koronis, Lester, Lydick,
Mohawk, Razort and Taopi soils do not have soil sa ration in the lower third of the
series control section for more than 1 consecutive m nth. The Bassett, Caleb, Orwood,
and Sebbo soils do not have free carbonates above a epth of 48 inches. Dowagiac soils
have sandy outwash sediments with less than 10 per ent clay in the lower third of the
series control section. Dunbridge and Winneshiek so ls have sola terminated by limestone
bedrock at depths of 20 to 40 inches. Lauramie soils re dry in some parts of the soil
moisture control section for less than 60 days during he 120 days following the summer
solstice. Longlois soils have 15 to 60 percent rock fr gments in the lower half of the
series control section. Neda and Racine soils have le s than 30 percent sand in the upper
one fourth of the series control section. Newcomer, neco and Waucoma soils have sola
terminated by a lithic contact at depths of 40 to 60 in hes.
GEOGRAPHIC SETTING: These soils have conv x slopes on moraines or till plains.
Slopes range from 2 to 5 percent. They formed in ca areous, loamy glacial till of late
Wisconsin Age. Mean annual air temperature ranges from 45 to 50 degrees F. Mean
annual precipitation ranges from 25 to 32 inches. Fr st-free days range from 125 to 165.
Elevation above sea level ranges from 700 to 1600 f t.
GEOGRAPHICALLY ASSOCIATED SOILS: T ese includes the Cordova, Dundas,
Glencue, Hamel, Hou�iton, Klossnci�, and Le Sueur oils which formed in similar parent
materials. Poorly drained Cordova and Dundas soils re on flats and upper drainageways.
Very poorly drained Glencoe soils are in depressions and drainage channels. Poorly
drained Hamel soils are on footslopes or toeslopes. ery poorly drained Houghton and
Klossner soils are organic and are in depressions. M derately well drained Le Sueur soils
are on slightly elevated flats and less sloping area.
DRAINAGE AND PERMEABILITY: Well drain d. Permeability is moderate. Runoff
is low. A seasonal high apparent water table is at 3.5 to 6 feet during March to June in
most years.
USE AND VEGETATION: Mostly cropped to co and soybeans. Native vegetation is
mixed prairie grasses and deciduous forest.
DISTRIBUTION AND EXTENT: South-central a d east-central Minnesota and
possibly northeastern Iowa. Moderate extent. ML -103.
MLRA OFFICE RESPONSIBLE: St. Paul, Minn ota
SERIES ESTABLISHED: Meeker County, Minne ta, 1995.
REMARKS: Diagnostic horizons and features reco nized in this pedon are: mollic
subgroup - the zone from the surface to a depth of 8 nches (Ap horizon); argillic horizon
- the zone from 8 to 35 inches (Bt horizons); This so was previously included in the
Lester series. However, due to more investigations, i was concluded that Lester soils on
a slope of 2 to 5 percent have seasonal high water ta le between 3.5 and 6 feet rather than
6 feet or greater.
ADDITIONAL DATA: Soil Interpretation Record umber MN0830.
i
KILKENNY SERIES
The Kilkenny series consists of very deep, moderate y well drained soils that formed in a
mantle of clayey glacial till or flow till and underlyi g loamy glacial till on moraines.
These soils have moderately slow permeability. The r slopes range from 2 to 35 percent.
The mean annual precipitation is about 28 inches. an annual air temperature is about
48 degrees F.
TAXONOMIC CLASS: Fine, smectitic, mesic Ox aquic Vertic Hapludalfs
TYPICAL PEDON: Kilkenny clay loam with a 15 ercent linear sideslope on a�lacial
moraine in a pastured field. (Colors are for moist so' unless otherwise noted.)
Ap--O to 9 inches; very dark brown(lOYR 2/2) clay loam, dark grayish brown(lOYR
4/2) dry; weak fine granular structure; friable; com on very fine roots; about 2 percent
gravel; moderately acid (pH 5.6); abrupt smooth bo ndayr. (6 to 10 inches thick)
Btl--9 to 19 inches; brown(lOYR 4/3) silty clay lo ; moderately medium subangular
blocky structure parting to moderately fine subangu ar blocky; firm; common fine and
very fine roots; few distinct very dark brown(lOYR 2/2) clay films on faces of peds;
about 3 percent gravel; strongly acid; gradual wavy oundary.
Bt2--19 to 38 inches; brown(lOYR 4/3) clay loam; oderate medium prismatic structure
parting to moderate medium subangular blocky; fi ; common very fine roots; common
distinct very dark brown(lOYR 2/2) clay films on f ces of peds; about 5 percent gravel;
strongly acid; gradual wavy boundary.
Bt3--38 to 53 inches; brown(lOYR 4/3) clay loam; eak medium subangular blocky
structure parting to weak fine subangular blocky; fi ; common distict very dark brown
(lOYR 2/2) clay films on faces of peds; about 5 per ent gravel; few fine distict brown
(7.SYR 4/4) Fe concentrations; moderately acid; gr ual smooth boundary. (Combined
thickness of the Bt horizons is 20 to 40 inches.)
2BC--53 to 65 inches; light olive brown(2.SY 5/4) oam; weak fine subangular blocky
structure; few distinct dark brown(lOYR 3/3) clay lms on faces of peds; friable; about 8
percent gravel; about 2 percent cobbles; few fine di tinct brown(7.SYR 4/4) Fe deletions;
slightly effervescent; slightly alkaline; gradual wav boundary.
2G-65 to 80 inches; light olive brown(2.SY 5/4) lo m; massive; friable; few
concentrations of light gray(2.SY 7/2) calcium carb nates in pores; brown(7.SYR 4/4)
soft masses of iron-manganese in nodules; about 8 ercent gravel; about 2 percent
cobbles; common medium prominent dark yellowis brown(lOYR 4/6) Fe
concentrations and common medium distinct gray( .SY 5/1) Fe depletions; strongly
effervescent; moderately alkaline.
TYPE LOCATION: Le Sueur County, Minnesota; about 3 miles west and 3 miles south
of Montgomery; about 300 feet east and 800 feet no h of the southwest corner of Sec.
�
19, T.111N., R.23W.; USGS Montgomery quadrang e; lat. 44 degrees 24 minutes 3
seconds N., and long. 93 degrees 38 minutes 41 sec ds W.,NAD 27.
RANGE IN CHARACTERISTICS: Depth to free arbonates range from 20 to 60
inches. Gravel of mixed lithology, but dominated by shale fragments, typically make up 2
to 8 percent of the volume of the series control secti n, but the upper part of the profile in
some pedons contains less than 2 percent gravel. Ro nded shale fragments dominate the
coarse sand fraction. Soil saturation occurs above a epth of 40 inches in 6 out of 10
years.
The Ap or A horizon has hue of lOYR, value of 2 or 3 and chroma of 1 or 2. It is clay
loam, silty clay loam, loam or silt loam. The reactio is moderately acid to neutral.
Some pedons have a thin E horizon.
The Bt horizon has hue of lOYR or 2.SY, value of 4 r 5, and chroma of 3 to 5. Faint to
prominent Fe concentrations and depletions commo ly are above a depth of 40 inches.
Redox depletions do not occur in the upper 10 inche of this horizon. The upper 20
inches of the Bt horizon typically contains 35 to 45 ercent clay. B/A clay ratios are 1.2
to 1.4. The Bt horizon is clay loam, silty clay loam, r clay. The reaction strongly acid to
neutral.
The 2BC horizon has properties similar to the 2C ho izon. Some pedons have a 2BK
horizon.
The 2C horizon has hue of lOYR or 2.SY, value of or 5, and chroma of 2 to 5. It is clay
loam or loam. The reaction is slightly alkaline or mo erately alkaline.
COMPETING SERIES: There are no competing s ries.
GEOGRAPHIC SETTING: Kilkenny soils have p ane and convex slopes on gently
sloping to steep end moraines of the Des Moines lob of the Late Wisconsinan glaciation.
Their slopes range from 2 to 35 percent. They forme in a mantle of clayey glacial till or
flow till and underlying loamy glacial till on morain s. Mean annual temperature ranges
from 45 to 52 degrees F. Mean annual precipitation 's about 25 to 32 inches. Frost-free
days range from 145 to 175. Elevation above sea lev 1 ranges from 800 to 1500 feet.
GEOGRAPHICALLY ASSOCIATED SOILS: T ese are the Glencoe, Lerdal, Lester,
Le Sueur, Lura, Mazaska, and Shields series. The ve y poorly drained Glencoe and Lura
soils are in the lower lying drainageways and depres ions. The somewhat poorly drained
Lerdal soils are on gently sloping to moderately stee areas. Shields soils are poorly
drained, and are on slightly elevated flats. Mazaska ils are poorly drained, and are on
slightly elevated flats and swales above or within ar s of Kilkenny soils. Also, the well
drained Lester soils and the moderately well drained Le Sueur soils are associated in a
few areas.
DRAINAGE AND PERMEABILITY: Moderatel well drained. Permeability is
moderately slow. Runoff is medium to very high. A erched seasonal high water table
occurs at depths of 2.5 to 4.0 feet during the period pril, May, and June in normal years.
I
USE AND VEGETATION: Most of these soils are cropped to corn, grain, hay, and
soybeans. Some areas are used for pasture and some are forested. Native vegetation is
mixed prairie and forest species.
DISTRIBUTION AND EXTENT: South central innesota and north-central Iowa. The
series is of moderate extent.
MLRA OFFICE RESPONSIBLE: St. Paul, Minn sota
SERIES ESTABLISHED: Waseca County, Minne ota, 1963.
REMARKS: Diagnostic horizons and features reco nized in this pedon are: Ochric
epipedon- the zone from the soil surface to a depth f 9 inches(Ap horizon); Argillic
horizon-the zone from 9 to 53 inches (Btl, Bt2, Bt horizons); Oxyaquic subgroup
based on saturation above a depth of 40 inches; Vert c subgroup based on more than 6 cm
of COLE in upper 40 inches. Water table studies an field observations have verified a
perched condition in most years, particularly in peri ds of extended rainfall.
ADDITIONAL DATA: Soil Interpretation Record umber MN0376.
KLOSSNER SERIES
The Klossner series consists of very deep,very poorly drained oils formed in weli decomposed organic
material 16 to 50 inches thick overlying loamy deposits on mor ines,till plains, lake plains,flood plains,
and hillside seep areas.They have moderately slow to moderat ly rapid permeability in the organic
material,and moderate or moderately slow permeability in the amy material. Slopes range from 0 to 8
percent.Mean annual precipitation is about 28 inches.Mean an ual temperature is about 47 degrees F.
TAXONOMIC CLASS: Loamy, mixed, euic, mesi Terric Haplosaprists
TYPICAL PEDON: Klossner muck- with a 1 perc nt slope in a cultivated field. (Colors
are for moist soil unless otherwise stated.)
Oap--O to 10 inches; black (N 2/0) muck, very dark ray(lOYR 3/1) dry; about 20
percent fiber, less than 5 percent rubbed; weak fine s bangular blocky structure; very
friable; many very fine roots; moderately acid; abrup smooth boundary.
Oa--10 to 26 inches; black(lOYR 2/1)muck, dark g ay(lOYR 4/1) dry; about 60 percent
fiber, about 6 percent rubbed; weak fine subangular locky structure; very friable; many
very fine roots; moderately acid; gradual smooth bo dary. (Combined thickness of O
horizon is 16 to 50 inches.)
2A1--26 to 36 inches; black(N 2/0)mucky silty cla loam; weak medium subangular
blocky structure; friable; few very fine roots; slightl acid; gradual smooth boundary.
2A2--36 to 48 inches; black(N 2/0) silty clay loam; assive; friable; few dark reddish
brown(SYR 3/4) iron oxide concentrations in root c annels; about 1 percent gravel;
neutral; gradual wavy boundary. (Combined thickne s of 2A horizon is 8 to 45 inches
thick.)
2Cg1--48 to 65 inches; olive gray(SY 5/2) clay loa ; massive; friable; dark reddish
brown(SYR 3/4) Fe oxide concentrations in root ch els; many medium prominent
yellowish brown(lOYR 5/6) Fe concentrations; abo t 1 percent gravel; slightly
effervescent; slightly alkaline; gradual wavy bounda .
2Cg2--65 to 80 inches; gray(SY 5/1) loam, massive; friable; many medium prominent
light olive brown(2.SY 5/4) and yellowish brown(1 YR 5/4) Fe concentrations; about 3
percent gravel; slightly effervescent; slightly alkalin .
TYPE LOCATION: Nicollet County, Minnesota; 2 00 feet north and 2300 feet east of
the southwest corner, sec. 12, T. 110 N., R. 28 W.; SGS Nicollet quadrangle; lat. 44
degrees 20 minutes 53 seconds N. and long. 94 degr es 8 minutes 28 seconds W.,
NAD27.
RANGE IN CHARACTERISTICS: The thickness of the organic material ranges from
16 to 50 inches. It is derived primarily from herbace us plants. The organic matter
content ranges from 25 to 60 percent in the organic s rface and 5 to 20 percent in the 2A
horizon. The reaction of the organic material ranges om moderately acid to slightly
alkaline. Some organic layers contain free carbonate .
The O horizon has hue of lOYR, SYR, or is neutral, alue of 2 or 3 and chroma of 0 to 2.
It is dominantly muck(sapric material) however, so e pedons have thin layers of hemic
material, less than 10 inches thick.
Some pedons have highly organic mineral plow laye s.
The 2A horizon has hue of lOYR, 2.SY, SY or is ne tral, value of 2 or 3 and chroma of 0
to 1. It is loam, silt loam, sandy clay loam, silty clay oam, clay loam or mucky modifiers
of these textures. It is moderately acid to slightly alk line. Some pedons contain thin
layers of coprogenous earth.
The 2Cg horizon has hue of lOYR, 2.SY, SY, SGY, r is neutral, value of 2 to 7 and
chroma of 0 to 2. It is loam, silt loam, silty clay loa , clay loam, sandy clay loam, sandy
loam or fine sandy loam, or their gravelly or cobbly nalogues. It is slightly acid to
moderately alkaline. The upper 12 inches of this ho ' on averages less than 35 percent
clay. Some pedons contain thin strata of fine sand, 1 amy sand, or silt. Gravel or cobble
sized rock fragments range from 0 to 25 percent by lume. Some pedons contain free
carbonates. Sandy substratum and ponded phases ar recognized.
COMPETING SERIES: These are Linwood, Med<, Palms, Philbon and Sl�alcae series.
Linwood soils have well expressed granular structur to depths of more than 12 inches
and formed mainly in woody fibers. Medo soils hav sandy textures in the lower part of
the series control section. Palms soils have organic atter content greater than 75 percent
and do not have an A horizon directly below the org nic material. Philbon soils have
fibric and hemic material in the upper 12 inches. Sha car soils ave less than 26 degrees
difference between mean January and mean July tem eratures.
GEOGRAPHIC SETTING: Klossner soils are in b sins that were formerly lakes or
ponds, lake plains, till plains, flood plains, or morain s. They are also on hillside seep
areas in moraines and sideslopes of river valleys. Slo es range from 0 to 8 percent. The
soils on nearby uplands are generally loamy. The me n annual temperature ranges from
45 to 50 degrees F. The mean annual precipitation ra ges from 24 to 32 inches. Frost free
days range from 110 to 160. Elevations above sea le el range from 800 to 1400 feet.
GEOGRAPHICALLY ASSOCIATED SOILS: T e main ones are the Canisteo, Hat-ps,
Okoboji, Glencoe, Muske<„o and Hou�.:hton soils. Ca isteo and Harps soils are on the rims
of depressions. Glencoe and Okoboji are at the outer edges of the depressions. Muskego
and Houghton soils are in larger depressions.
DRAINAGE AND PERMEABILITY: Very poorl drained. Surface runoff is
negligible. Permeability is moderately slow to mode tely rapid in the organic layers and
moderate or moderately slow in the loamy material.
USE AND VEGETATION: The greater part of this soil is cultivated to corn, soybeans,
small grains and specialty crops such as vegetables o grass sod. Other areas are in
vegetation of grasses, reeds, sedges, alder, aspen, or illow. Some of the hillside seep
areas are set aside as natural areas and called fens.
DISTRIBUTION AND EXTENT: The south centr 1 and southeast part of Minnesota
and possibly northern Iowa. The series is extensive.
MLRA OFFICE RESPONSIBLE: St. Paul, Minn sota
SERIES ESTABLISHED: Nicollet County, Minne ota, 1989.
REMARKS: Diagnostic horizons and features reco nized are: sapric soil materials from
the surface to about 26 inches; loamy mineral materi 1 from 26 to 50 inches or more;
aquic moisture regime. This soil was formerly inclu ed in the Palms Series in Minnesota.
ADDITIONAL DATA: Refer to MAES-CFC#'s 26 7, 3251, 3400 and 3475.
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Wetland 1
Overview of wetland taken from north facing south. Wetland is a reed canarygrass and cattail wet meadow with a
dredged open area on the east side of the wetland that adjoins an open water semipermanently inundated pond to
the east of the parcel.
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Wetland 1
Overview of wetland upland transition taken from the west side of the wetland facing north. Land slopes down from
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Wetland 1
Seasonally inundated wetland taken from roughly sample point SP 1-1 Up facing south over fence with SP 1-1 Wet
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Wetland 1
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Photo showing dredged open water area and resulting sidecast wetland. The wetland area in the foreground is
mainly reed canarygrass and common milkweed sitting on a soil that was side cast from the dredged wetland area
in the background.
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1. Project/Site Infor ation
Project/Site Name: ��ke�o�ad�acen��o a2a,eays�de Rd Local G vernment Unit: City of Orono
Location (address and/or T, R, Sec.): Part of S Yz E %2 S % NE '/, Section 6, T117N, R23W
2. Applicant Infor ation
Applicant Name: VCI Capital ddress: Box 375
City, State, Zip: Long Lake, MN 55356
E-mail: robwhite@vcicapital.com hone: 952-476-2637
3. Agent/Consultant I formation
Company Name (if applicable): s�oboaa Ecoiog�cai Resources ontact Person: Frank Svoboda
Address: 25580 Nelsine Drive ity, State, Zip: Shorewood,MN,55331
E-mail: franks@gpsinnovations.com Phone: 952-471-1100
4. Description of R quest
Check all that apply: 0 Wetland Boundary(musl attach w tland delineation repori)
O Wetland Type (Eggers & Reed an /or Circular 39 type)
5. Signatur
By signature below, the applicant requests a determination from the Local Government Unit under
Minnesota Rules 8420.0225 on the submitted wetland bou dary and type information in this application.
The applicant also affirms that they are the owner o( the su ject property or have permission from the
landow er to pursue this determin i�n.
/ '/
� `�G12 ��i / ,�._-- �����"//�-.
Applicant or Authorizec�A ent ignature Date
Important Notes:
• The applicant may be required to submit mul iple copies of the report/information to the
LGU. The LGU may require the applicant to ubmit copies directly to Technical Evaluation
Panel Members. Check wifh your LGU reg rding their submitfal requirements.
• The LGU decision must be made in complia ce with Minnesota Statutes, section 15.99.
For LGU use only
Date Received:
Page 1 of 1
BWSR Wetland Boundary/Type Application Form 11/10/08
Print Form
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i s ���„� c�����ti
��r e�,,t����.���,
\t.Paul I)iVricl
Request fo�• Corps of En�;inecrs ��'c land Dclineation Re�•ic��
Pl�a;� :iit�r th� fi�llu��in�� `��iicr,�l infurmatiun ah��ut thc ��ru���rt� tuxlcr rc�i���:
\amc of pi•opert� o��ncr
VCI Capital
Properh :�dclress (\c�. S Street. Cit�, Stute. Lip C ode) -----
XXXX Bayside Road (Vacant Lot Adjacent to d2A5 Bayside Rd)O ono. N1N 55356
----_.__.._--------------__......_ ______.......__---- --..__- ---.
Lat. _ l.on�;. _ (dccim.� dc�Trces) -____-
Counh Hennepin
---- ------- ---__.___----- - ----- --__
Locatiun: NE 1l-1 Scction 6 �I'u���nship 117N an;;c 23W
------_—.._._-__._.._----------.._------ -__..___. ___.._._..._._...__..__------
Sizc of rc�ic�� arc.i 1 1 acrc(s)
l3� ;ubmi;;iui� ��f thi; ���tlan�l �lclin�;�tic�n i������i-t I 1t111 I'cl�ll�iClll`, that [hc l!.�. \rin� ('ur��, ��t�f:n;;in��r;. �t.
I';�ul I)i;h�i�t ��r���i�l� n�� ��ith tl�c tullu��in_f Ich�ck unl� onc f u.�l: "
❑ �1 ctlan�l U�lin���tiun Cunc�n�r�n��. C'un�urr�n�c ��ith ���� tlun�l �Iclin�.itiun i; a ��ritt�n nutiti�,itiun f�rc,il�
th� C�l�l'�l� Ct)Il�lll'I'III�L Ilt�t CUIICUI'I'lll`,. ��I'C��Illlll�l)[III;� t�ll [Il� Ctlan�l huun�l�iri�;�I�lin�a���l c�n a ��ru���rt�.
l!n�lcr thi: r�yu�;t. ih� ����r��; ��ill nut .i�1�fr�,; th� juri;�iictiun�I ;t,itu>��t�th� ���tlai�ch un thc ��n����rt�. unl�
thc hc�un�iaric; ��I�thc r�;�xn�cc; ��ithin thc r��i.:�� �u��a.
✓0 Pr�liminar� J�n-i;clictiui�al [��t�rniin�jtiui�. f'rcliminarv Ju�i;clictiui�al f)ct�i�mii�ati��ii. .\ ��ecliminarv
juri;cli�ti��n.il �1ct�rminc�ti�ii� i; a nunhinclii��� ��ritt�i� iiulirati��i that thcr� m,i� b� ��atcr; ��t�tl�� l!nit�cl Stal��.
ii��lu�lin�� ���ctlancl,. on a p.ircel ur in�lirati��n; of th� a��pru�in at� lucatiunl;) ��f���at�i•; ot th� U«it��1 �tat�, ��r
«�tl.11lll� vll �; ��a�r�L f=��r� �ur�x�;c:, uf r��mptuati�>n ot�impact, an�l cc�in��cn;��t��ry mi;i`�at;��n r�i�uir�inc�,t: a
�i�rmit �ic�i;i��n ma�lc ��n thc b��;i: uf a ��r�lii»ii�ar��juri;�lictic>>al cict�rminatiun ��ill trcat all «��tcr; an�1
���tlan�l, in th� r�� ic�� ar�a a, if thcy ��rc,juri>clicti��nal ��at�r_ ��fthc l!.S. Pr�liiniiiar� luri;dictic�nal
�Ictcrmin�uiu��s �u�� a�l�i;or� in nann�� an�i ma� iiut b� upp�alc l.
❑ :�����ru���i Juri;�li�ti��nill I)CI�I'llllll,�ti�in. \n ,�����ru�c�l,jui�i.�lictional �Ictcrminati��n i; an o��1i�i,�l ('ur��;
�I�t�rn�in;�ti�iii th;�t juri,�lirtiun.il ��at�r; c�f th� �`nit��l St,�tc; u' nu�i`_ablc ��at�r;ul�th� l nit�ci Stat��, ur h��tl�.
�lI'�CI[Il�f (11'C1�11[ lll'lt�)��Ill llll lll� ��r����crt�. .\n a����r���ccl jur ;�lirti��n�ll lIC[�I'llllllatiun ��rcri:�l� i�l�ntiti�; th�
limit; uf th���� ��at�r� ut� thc E�rujcct ;it� �I�t�rinin.�l tu h� juri �lirtiun,il un�lcr thc C'I�:ii� \1�ater \�t ur IZi��r;
an�1 I I.�rh��r; :\rt. .\����ru�c�l juri;�li�tiunal �1ct�r�iiinati�,n; cai b� r�li�cl u��un hy thc al�l�rt.�l ��urtv ti�r:�
��criucl ut ti�c ��ar,. .\n ap��ru���I juri;cli�tiunal �1�t�rminati�>> ma� h�u����a�lc�l thruu`,h th� ('ur4�;'
a�linini;trati�� a�����al ��i�ur�;;.
In urcl�r fur thc ('ur��; tu ��rc�r�,: �uur r�qu�;t. th� ���tlai��l �I� in�atiun mu,t h� pr���ar�c1 ii� u«ur�lan�� ��ith
th� I`)�� C'��r��; uf I;n`_in�er; \�'�tlaiul l)�lincatiun �1.u�uaL .►i � a����r���c�1 R�`�iunal �u����l�mcnt; ic> �hc l�)�?
�•1.inuaL an�l th� t;ui�lelines ti�r Suhmithn4� 11�tlancl Ihlii���it ��n; in \lii�ne;uta an�1 1\ i;cun;in
i htt��: ������.in�p.us�ir�.armv.mil r���u atur` ►.
"�•, 10/1=1;13
� nat�
Requ�;tc�r ' ��',/y��.�I�1i. �_
\�imc (t�p��l)�ranklin J. Svoboda
Hennepin County GIS - Printable Map � Page 1 of 1
Interacti�e PrOpel�ty
_. , Maps Map
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Parcel 06-117-23-13-0003 A-T-B: Both Map Scale: 1"=400 ft. N
ID: �Print Date: 10/25/2013
Owner Veda Inc Market $698,000
Name: Total:
Parcel 38 Address Unassigned Tax $9,522.48
Address: Orono, MN 00000 Total: (Payable: 2 13)
Property Vacant Land-Lakeshore Sale '
Typ@: PI'IC@: This map is a compilation of data from various
sources and is furnished"AS IS"with no
HOme- Sale representation or warranty expressed or
stead: Non-Homestead Date: implied,including fitness of any particular
purpose,merchantability,or the accuracy and
completeness of the information shown.
Parcel 11.86 acres Sale
Area: 516,470 sq ft COd@: COPYRIGHT OO HENNEPIN COUNTY 2013
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http://gis.co.hennepin.mn.us/Property/print/default.aspx?C= 50320.0844938404,4980070... 10/25/2013