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Prouiding the Sharper Edge in
Natural Resources & Environmental Consulting
ECOL�GICAL RES�URC.ES
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4565 Ba side Rd
Y
Orono, Hennepin County, l�'IN
Wetland Classification, Identification, and
Delineation Report
Prepared for:
Peter and Sharon Rennebohn
By:
Svoboda Ecological Resources
Project Number 2014-022
September 22, 2014
The contents and format of this report are considered intellectual property and
are subject to copyright restrictions and may not be reproduced without
the express permission of Svoboda Ecological Resources.
Table of Contents
ABSTRACT.................................................................................................................................................1
INTRODUCTION.......................................................................................................................................1
METHODS..................................................................................................................................................1
RESULTS.......................................................................................................................:.............................2
DISCUSSION..............................................................................................................................................4
RECOMMENDATIONS............................................................................................................................4
CERTIFICATION......................................................................................................................................5
DATASOURCES........................................................................................................................................6
LITERATUREREFERENCED................................................................................................................7
FIGURES:
Figure 1: Site Location Overlaid on Topographic Map
Figure 2a: National Wetland Inventory
Figure 2b: Hennepin County Wetland Inventory
Figure 2c: 2014 DNR NWI Update
Figure 3: Web Soil Survey-Hennepin County
Figure 4: Public Waters Inventory
Figure 5: Approximate Wetland Boundary and Sample Point Location
Figure 6:Approximate Wetland Boundary and Soils
TECHNICAL DOCUMENTS:
Photo Log
Field Data Sheets
P1antIndicator Status
Soil Series Data
ABSTRACT
Svoboda Ecological Resources (SER) visited the above referenced property on 9/13/14 to
examine the site for the presence of areas meeting wetland criteria. The study parcel is located in
the city of Orono, MN in Hennepin County (Figure 1). Two wetland boundaries were delineated
at this site. Two sample transects were established (one each) along the boundaries of the
wetland area coming onto the northwest corner of the properry and the depressional wetland on
the eastern side of the properry in order to characterize the soil, vegetation, and existing
hydrology within the wetland-to-upland transition zone.
INTRODUCTION
The subject parcel at 4565 Bayside Rd is approximately 9.66 acres. The parcel is dominated by
upland woods and open meadows, (all open areas are well groomed), where the domestic
structure is present, as well as two small wetlands and a ravine. The surrounding land use is
primarily widely to closely-spaced single family homes interspersed with wetlands. The
identified wetland was classified according to the Cowardin et al., the Circular 39 and the Eggers
and Reed classification systems and marked with pink "Wetland Delineation" pin flags. The
Technical Documents section of this report contains field data sheets, plant indicator status
information, soil survey information, and wetland definition information.
METHODS
The methods used to delineate the subject parcel are as described in the 1987 US Army Corps of
Engineers Wetlands Delineation Manual and the 2010 Midwest Regional Supplement Manual. In
the 1987 Manual, the methods used were described under the "routine" methods for sites less
than 5 acres. This methodology is followed in order to assess whether the three parameters of a
wetland are met for areas on the subj ect parcel. The three parameters required under normal
circumstances in order to delineate a wetland are described in the Technical Documents section.
The Midwest Regional Supplement Wetland Delineation Manual is also being utilized to
increase the accuracy of our wetland boundaries. This addendum to the original 87 Manual was
created to address the many regional differences that affect wetlands and the delineation methods
used throughout the country. The following explanations are passages from that document.
"This Regional Supplement is part of a nationwide effort to address regional
wetland characteristics and improve the accuracy and efficiency of wetland-
delineation procedures. Regional differences in climate, geology, soils,
hydrology plant and animal communities, and other factors are important to the
identification and functioning of wetlands. These differences cannot be
considered adequately in a single national manual. The development of this
supplement follows National Academy of Sciences recommendations to increase
the regional sensitivity of wetland-delineation methods (National Research
Council 1995). The intent of this supplement is to bring the Corps Manual up to
date with current knowledge and practice in the region and not to change
wetland boundaries." "...This Regional Supplement is designed for use with the
current version of the Corps Manual (Environmental Laboratory 1987) and all
Svoboda Ecological Resources 1 4565 Bayside Road
Project Number:2014-022 Orono,MN
subsequent versions. Where differences in the two documents occur, this
Regional Supplement takes precedence over the Corps Manual for applications
in the Midwest Region."
National Wetland Inventory (NWI) maps (Figure 2a) Hennepin County Wetland Inventory
(HCWI) maps (Figure 2b), 2014 DNR NWI Update maps (Figure 2c), Web 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 that may be wetlands.
Areas illustrating evidence of wetland conditions were examined in greater detail during the field
survey. Vegetation, soils and hydrology were examined (as outlined in the 1987 Manual) and
used to characterize wetland types and determine wetland boundaries. Sample transects were
established in representative wetland-to-upland transition zones in order to characterize the
vegetation, soils, and hydrology of the site. Transects consist of a representative upland sample
point and representative wetland sample point. Information obtained 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 pink "Wetland Delineation" pin flags. The
wetland boundary is considered to be the topographically 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 were classified in accordance with methods
described by Cowardin et aL (1979) and used in the NWI (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, as described in the Technical Documents
section, was determined using the National Wetland Plant List (Lichvar, et al. 2014.
httn://wetland plants.usace.armumil�.
RESULTS
The National Wetland Inventory indicates the presence of no wetlands in the survey area (Figure
2a). The HCWI indicates the probable presence of 1 wetland in the survey area, in the
northwestern corner (Figure 2b). The DNR NWI update in 2014 also indicates the presence of
one wetland in the northwest corner of survey area, categorized as PEM1A(Figure 2c).
The Web Soil Survey of Hennepin County (Figure 3) identifies five soil map units present on the
subject property. They are as follows: Hamel, overwash-Hamel complex; Angus-Kilkenny
complex; Lester loam, morainic; and two Lester-Kilkenny complexes, eroded, of different
slopes. The Hamel soil is partially hydric while the remaining types are predominantly
nonhydric. Soil series descriptions are provided in the Technical Documents section.
The Minnesota Department of Natural Resources, State Protected Waters Map (Public Waters
Inventory) indicates no public waters within the study area(Figure 4).
Site Visit
SER ecologists examined the subject property for areas meeting jurisdictional wetland criteria
during the site visit. Two areas meeting the jurisdictional criteria of a wetland were flagged, and
boundaries were determined and delineated. The approximate wetland boundaries are outlined in
yellow (Figures 5 and 6).
Svoboda Ecological Resources 2 4565 Bayside Road
Project Number:2014-022 Orono,MN
Accumulated precipitation since 4/Ol/2014, as recorded at MSP and reported by the USDA
National Agricultural Statistics Service in cooperation with the Minnesota Department of
Agriculture reports that for the week ended September 14, 2014, was 7.67" above normal.
Precipitation for the period 9/8/14 to 9/14/14 was reported to be 0.54" below normal and for the
preceding 4 weeks was 1.27" below normal.
The 2014 DNR NWI update identified the wetland area in the northwest carner as PEM1A. The
wetland is a temporarily flooded or saturated wet meadow, dominated by emergent herbaceous
vegetation. We would agree with this classification (Eggers and Reed Classification — Wet
Meadow; Circular 39 Type 2). Vegetation in the seasonally inundated wetland was dominated by
reed canarygrass (Phalaris arundinacea FACW). Transition to uplands is marked by slope and
increased woody vegetation.
Transect SP 1-1 was taken from the southeastern boundary of the wetland. The soils at sample
point SP 1-1 Wet consisted of dark loam clay layers at the surface with a depleted silt clay
beneath. Hydric indicators Al2 (Thick Dark Surface) was present. The soils at sample point SP
1-1 Up consisted of several loam layers at the surface with a loam clay below. No hydric
indicators were.
At sample point SP 1-1 Wet secondary hydrology indicators D2 (Geomorphic Position) and DS
(FAC Neutral) were present. Wetland hydrology was not indicated at sample point SP 1-1 Up.
The eastern depressional wetland was not identified by any wetland inventories. The wetland is a
temporarily flooded or saturated wet meadow, dominated by emergent herbaceous wetland. We
would likely classify this as PEMIA in the Cowardin classification system (Eggers and Reed
Classification — Wet Meadow; Circular 39 Type 2). Vegetation in the seasonally inundated
wetland was dominated by reed canarygrass (Phalaris arundinacea FACW). Transition to
uplands is marked by slope and, in some areas, increased woody vegetation.
Transect SP 2-1 was taken from the northern boundary of the wetland. The soils at sample point
SP 2-1 Wet consisted of dark loam layers at the surface with loam depleted loam clays below.
Hydric indicators A11 (Depleted Below Dark Surface) and F7 (Depleted Dark Surface) were
present. The soils at sample point SP 2-1 Up consisted of several layers of loam, clay loam and
loam clay, often with redox concentrations or depressions present. Hydric indicator F8 (Redox
Depressions) was present.
At sample point SP 2-1 Wet secondary hydrology indicators D2 (Geomorphic Position) and DS
(FAC Neutral) were present. Wetland hydrology was not indicated at sample point SP 2-1 Up.
A deeply incised ravine with steep banks is also present on the properry (Figures 5 and 6). It
begins at the eastern property line and continues in a southeasterly direction exiting the property
in the southeastern corner. The area was not delineated as it is a flowage that carries water only
during heavy rainfall or during spring snowmelt. It was mapped in order to comply with St. Paul
District Corps of Engineers documentation requirements.
Detailed soils, vegetation, and hydrology data for the delineated jurisdictional wetlands are
provided in the data sheets of the Technical Documents section.
Svoboda Ecological Resources 3 4565 Bayside Road
Project Number:2014-022 Orono,MN
DISCUSSION
SER completed all on-site delineations based on the three required technical criteria as outlined
by the 1987 Manual: the presence of hydric soils, a predominance of hydrophytic vegetation,
and indicators of wetland hydrology in each basin. The site visit portion of the wetland
delineation was completed on 9/13/14.
SER personnel examined the subject properties for areas meeting jurisdictional wetland criteria
during the site visit and delineated the edges of two wetlands as being jurisdictional wetlands
(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 section.
RECOMMENDATIONS
Activities that impact or could potentially impact wetlands are regulated at several levels of
government. In Minnesota, the two primary jurisdictions are covered at the state and federal
levels by the provisions of the following legislative actions.
�• State jurisdiction by the Wetland Conservation Act of 1991 (WCA) administered by the
WCA Local Governmental Unit (LGU).
z* Federal jurisdiction by the Clean Water Act of 1972 and subsequent amendments.
Wetland protection is implemented by the Corps of Engineers (Corps) with permit
certification issued by the Environmental Protection Agency.
While the wetland boundaries that SER has delineated are not official until approved by a WCA
approved local government unit (LGU), SER advises the property owner/developer to refrain
from any filling, draining, or excavating, or any impact to the area SER has delineated as
wetland. No grading or filling in wetland basins should commence until all necessary permits
have been obtained. Violation of wetland regulations may result in substantial civil and criminal
penalties. Local ordinances may regulate wetland modifications such as brush and tree removal
and burning in addition to grading and filling. Depending on the location of the property, buffers
around the wetland may also be protected. Any activities 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 the pin flags used along the boundary can
be vandalized or inadvertently knocked over, a GPS survey of the flags will assure the
permanence of the boundary. The client should also be aware that approved wetland boundaries
are typically valid for five years from the date of approval.
To avoid project delays associated with wetland regulations, it is essential that you acquire
necessary permits from all jurisdictional agencies before initiating activities. A WCA Sequencing
form, a WCA and Army Corps of Engineers Replacement Plan Application form, and a DNR
permit application are among the materials that you may be required to submit if impacts are
proposed for the delineated wetlands. By initiating the permit process as soon as possible,
potential costly delays to the project may be avoided.
Svoboda Ecological Resources 4 4565 Bayside Road
Project Number:2014-022 Orono,MN
CERTIFICATION
Frank Svoboda flagged the above-described wetlands on 9/09/14 and field data was collected by
David Remucal on 9/13/2014. This delineation was performed according to the procedures
described by the US Army Corps of Engineers in the 1987 Wetlands Delineation Manual and the
2010 Midwest Region Supplement Wetland Delineation Manual. The delineation meets the
standards and a criterion described in these manuals and conforms to the applicable standards
and regulations in farce at the time the delineation was completed.
Report and graphics were prepared by David Remucal (Wetland Ecologist) on this day 9/20/14.
The delineation report was reviewed by Frank Svoboda, President of Svoboda Ecological
Resources.
Client: Peter and Sharon Rennebohn
Project Name:4565 Bayside Rd
Project No.: 2014-022
Location: Orono, MN
� "
David Remucal, Wetland Ecologist
�� d�
President, Svoboda Ecological Resources
September 22, 2014
Date
Svoboda Ecological Resources 5 4565 Bayside Road
Project Number:2014-022 Orono,MN
DATA SOURCES
Minnesota Department of Natural Resources, Public Waters Inventory Basin Delineations,
Published 7/31/2008 and retrieved from http://deli.dnr.state.mn.us
United States Fish and Wildlife Service National Wetland Inventory Map. Retrieved from
http://www.fws.gov/wetlands/DatalMapper.html on 5/28/12.
2012 Aerial Color Photos. Publicly Distributed by MN Geo WMS Service.
Topographic maps obtained via the National Geographic Society's USA Topo service through
ESRI.
Web Soil Survey for Hennepin County, MN. Retrieved from
http://websoilsurvey.nre s.usda.gov/app/HomePage.htm
Svoboda Ecological Resources 6 4565 Bayside Road
Project Number:2014-022 Orono,MN
LITERATURE REFERENCED
Cowardin, L.M., V. Carter, F.C. Golet, and R.T. LaRoe. 1979. Classification of Wetlands and
Deepwater Habitats of the United States. U.S. Fish and Wildlife Service, FWS/OBS-79/31.
103pp.
Eggers, Steve D. and Donald M. Reed. 20ll. Wetland Plants and Plant Communities of
Minnesota and Wisconsin, Third Edition. US Army Corps of Engineers, St. Paul District. 478pp,
unclassified.
Environmental Laboratory. 1987. 1987 U.S. Army Corps of Engineers Wetlands Delineation
Manual. Technical Report Y 87-1, US Army Engineer Waterways Experiment Station,
Vicksburg, Mississippi.
Gleason, H.A. and A.C. Cronquist. 1991. Manual of Vascular Plants of Northeastern United
States and Adjacent Canada. New York Botanical Garden, Bronx. 910pp.
Lichvar, R.W., M. Butterwick, N.C. Melvin, and W.N. Kirchner. 2014.
The National Wetland Plant List: 2014 Update of Wetland Ratings.
Phytoneuron 2014-41: 1-42. http://wetland plants.usace.army.miU
Shaw, S.P., and C.G. Fredine. 1956. Wetlands of the United States. U.S. Fish and Wildlife
Service, Circular 39. 67pp.
U.S.Army Corps of Engineers.August 2010. Regional Supplement to the Corps of Engineers
Wetland Delineation Manual: Midwest Region (Version 2.0). ERDC/EL TR-10-16. Vicksburg,
MS: US Army Engineer Research and Development Center.
Svoboda Ecological Resources 7 4565 Bayside Road
Project Number:2014-022 Orono,MN
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THE TECHNICAL DOCUMENTATION SECTION
Field Data Sheets
WETLAND DETERMINATION DATA FORM -Midwest Region
Project/Site 4565 Bayside Rd City/County: Orono/Hennepin Sampling Date: 9-13-14
ApplicanUOwner: Peter and Sharon Rennebohn State: MN Sampling Point: SP 1-1 Up
Investigator(s): FJS, DR 3ection,Township, Range: T117N R23W S06
Landform (hilislope,terrace, etc.): hillslope Local relief(concave, convex, none): none
Slope(%): 2-3 Lat: Long: Datum: NAD83
Soil Map Unit NameAngus-Kilkenny complex, 2 to 6 percent slopes VWI Classification: None
Are climatic/hydrologic conditions of the site typical for this time of the year? N (If no,explain in remarks)
Are vegetation , soil , or hydrology significantly disturbed? Are"normal circumstances"
Are vegetation ,soil , or hydrology naturally problematic? present? Yes
SUMMARY OF FINDINGS (If needed, explain any answers in remarks.)
Hydrophytic vegetation present? Y
Hydric soil present? N Is the sampled area within a wetlan� N
Wetland hydrology present? N f yes, optional wetland site ID:
Remarks: (Explain alternative procedures here or in a separate report.)
Precipitation for week ending 9/08/2014 was 8.21"above normal since 4/01/2014,1.34"below normal for the preceding 4 weeks and 0..53"below
normal for the preceding week as measured at MSP and reported by the National Agricultural Statistics Service. Precipitation has been erratic in
2014-first extraordinaril wet and now relativel dr .Therefore the climatic conditions were recorded as"No".
VEGETATION -- Use scientific names of plants.
Absolute Dominan Indicator pominance Test Worksheet
Tree Stratum (Plot size: 30' ) %Cover t Species Staus Number of Dominant Species
1 Fraxinus pennsylvanica 40 Y FACW that are OBL, FACW, or FAC: 4 (A)
2 Pinus strobus 40 Y FACU Total Number of Dominant
3 Species Across all Strata: 5 (B)
4 Percent of Dominant Species
5 that are OBL,FACW, or FAC: 80.00% (A/B)
80 =Total Cover
Saplinq/Shrub straturr (Plot size: 15' ) Prevalence Index Worksheet
1 Rhamnus cathartica 20 Y FAC Total %Cover of:
2 OBL species 0 x 1 = 0
3 FACW species 40 x 2= 80
q FAC species 103 x 3= 309
5 FACU species 40 x 4= 160
20 =Total Cover UPL species 0 x 5= 0
Herb stratum (Plot size: 5' ) Column totals 183 (A) 549 (B)
1 Poa pratensis 80 Y FAC Prevalence Index=B/A= 3.00
2 Carex bicknellii 3 N FAC
g Hydrophytic Vegetation Indicators:
q Rapid test for hydrophytic vegetation
5 X Dominance test is>50%
g X Prevalence index is<_3.0"
7 Morphogical adaptations"(provide
g supporting data in Remarks or on a
9 separate sheet)
�p Problematic hydrophytic vegetation`
83 =Total Cover (explain)
WOOdY Vlne StfatUm (PIOt SiZe: 30� ) `Indicators of hydric soil and wetland hydrology must be
1 Parthenocissus quinquefolia 40 Y FAC present,unless disturbed or problematic
2 Vitis riparia 5 N FACW Hydrophytic
45 =Total Cover vegetation
present? Y
Remarks: (Include photo numbers here or on a separate sheet)
Carex not flowering
US Amy Corps of Engineers Midwest Region
SOIL Sampling Point: SP 1-1 Up
Profile Description: (Describe to the depth needed to document the indicator or confirtn the absence of indicators.)
Depth Matrix Redox Features
(Inches) Color(moist) % Color(moist) % Type* Loc" Texture Remarks
0-11 10YR 3/2 100 loam
11-14 10YR 3/2 70 10YR 6/1 30 D PL/M loam redox in soft masses
14-20 10YR 3/2 45 10YR 5/3 45 C PL/M loam
14-20 10YR 7/1 10 D PL
20-30 10YR 4/2 40 10YR 5/4 40 C M loam clay
20-30 10YR 2/1 20
*Type: C=Concentration, D= Depletion, RM= Reduced Matrix, MS= Masked Sand Grains. "Location: PL= Pore Lining, M= Matrix
Hydric Soil Indicators: Indicators for Problematic Hydric Soils:
Histisol(A1) Sandy Gleyed Matrix(S4) Coast Prairie Redox(A16)(LRR K, L,R)
Histic Epipedon(A2) Sandy Redox(S5) Dark Surface(S7)(LRR K,L)
Black Histic(A3) Stripped Matrix(S6) 5 cm Mucky Peat or Peat(S3)(LRR K,L,R)
Hydrogen Sulfide(A4) Loamy Mucky Mineral(F1) Iron-Manganese Masses(F12)(LRR K, L,R)
Stratified Layers(A5) Loamy Gleyed Matrix(F2) Very Shallow Dark Surface(TF12)
2 cm Muck(A10) Depleted Matrix(F3) Other(explain 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 must be present, unless disturbed or
5 cm Mucky Peat or Peat(S3) problematic
Restrictive Layer(if observed):
Type: Hydric soil present? N
Depth(inches):
Remarks:
HYDROLOGY
Wetland Hydrology Indicators:
Primarv Indicators(minimum of one is required: check all that applvl Secondar Indicators minimum of two re uired
Surface Water(A1) Aquatic Fauna(B13) Surface Soil Cracks(66)
High Water Table(A2) True Aquatic Plants(B14) Drainage Patterns(B10)
Saturation(A3) Hydrogen Sulfide Odor(C1) Dry-Season Water Table(C2)
Water Marks(61) Oxidized Rhizospheres on Living Roots Crayfish Burrows(C8)
Sediment Deposits(62) (C3) Saturation Visible on Aerial Imagery(C9)
Drift Deposits(63) Presence of Reduced Iron(C4) Stunted or Stressed Plants(D1)
Algal Mat or Crust(B4) Recent Iron Reduction in Tilled Soils Geomorphic Position(D2)
Iron Deposits(65) (C6) FAC-Neutral 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(B9) Other(Explain in Remarks)
Field Observations:
Surface water present? Yes No X Depth(inches): Wetland
Water table present? Yes No X Depth(inches): hydrology
Saturation present? Yes No X Depth(inches): present? N
(includes capillary fringe)
Describe recorded data(stream gauge, monitoring well, aerial photos, previous inspections), if available:
Remarks:
US Army Corps of Engineers Midwest Region
WETLAND DETERMINATION DATA FORM -Midwest Region
ProjecUSite 4565 Bayside Rd City/County: Orono/Hennepin Sampling Date: 9-13-14
ApplicanbOwner: Peter and Sharon Rennebohn State: MN Sampling Point: SP 1-1 Wet
Investigator(s): FJS, DR 3ection,Township, Range: T117N R23W S06
Landform(hillslope,terrace, etc.): depression Local relief(concave, convex, none): concave
Slope(%): 0 Lat: Long: Datum: NAD83
Soil Map Unit Name Lester-Kilkenny complex, 12 to 18 percent slopes,eroded VWI Classification: None
Are climatic/hydrologic conditions of the site typical for this time of the year? N (If no, explain in remarks)
Are vegetation , soil , or hydrology significantly disturbed? Are"normal circumstances"
Are vegetation , soil , or hydrology naturally problematic? present? Yes
SUMMARY OF FINDINGS (If needed, explain any answers in remarks.)
Hydrophytic vegetation present? Y
Hydric soil present? Y Is the sampled area within a wetlarn Y
Wetland hydrology present? Y f yes, optional wetland site ID:
Remarks: (Explain alternative procedures here or in a separate report.)
Precipitation for week ending 9/14/2014 was 7.67"above normal since 4/01/2014,1.27"below normal for the preceding 4 weeks and 0..54"below
normal for the preceding week as measured at MSP and reported by the National Agricultural Statistics Service. Precipitation has been erratic in
2014-first extraordinaril wet and now relativel dr .Therefore the climatic conditions were recorded as"No".
VEGETATION -- Use scientific names of plants.
Absolute Dominan Indicator pominance Test Worksheet
Tree Stratum (Plot size: 30' ) %Cover t Species Staus Number of Dominant Species
1 Pinus resinosa 10 Y FACU that are OBL, FACW,or FAC: 2 (A)
2 Total Number of Dominant
3 Species Across all Strata: 3 (B)
4 Percent of Dominant Species
5 that are OBL, FACW, or FAC: 66.67% (A/B)
10 =Total Cover
Saqlinq/Shrub straturr (Plot size: 15' ) Prevalence Index Worksheet
1 Sambucus canadensis 20 Y FACW Total %Cover of:
2 OBL species 0 x 1 = 0
3 FACW species 120 x 2= 240
q FAC species 0 x 3= 0
5 FACU species 10 x 4= 40
20 =Total Cover UPL species 0 x 5= 0
Herb stratum (Plot size: 5' ) Column totals 130 (A) 280 (B)
1 Phalaris arundinacea 100 Y FACW Prevalence Index= B/A= 2.15
2
3 Hydrophytic Vegetation Indicators:
q Rapid test for hydrophytic vegetation
5 X Dominance test is>50°/o
g X Prevalence index is<_3.0*
7 Morphogical adaptations"(provide
g supporting data in Remarks or on a
g separate sheet)
10 Problematic hydrophytic vegetation'
100 =Total Cover (explain)
WOOdV vin2 StfatUm (Plot SiZe: 30� ) `Indicators of hydric soil and wetland hydrology must be
� present,unless disturbed or problematic
2 Hydrophytic
0 =Total Cover vegetation
present? Y
Remarks: (Include photo numbers here or on a separate sheet)
Pine is Pinus nigra
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 absence of indicators.)
Depth Matrix Redox Features
(Inches) Color(moist) % Color(moist) % Type* Loc*" Texture Remarks
0-18 10YR 2!1 100 loam clay
18-24 10YR 2/1 97 10YR 4/1 3 D PL loam clay
24-30 10YR 6/1 40 10YR 7/5 20 C PL/M silt clay redox in soft masses
24-30 10YR 4/1 40
*Type: C=Concentration, D= Depletion, RM = Reduced Matrix, MS= Masked Sand Grains. `"Location: PL= Pore Lining, M= Matrix
Hydric Soil Indicators: Indicators for Problematic Hydric Soils:
Histisol(A1) Sandy Gleyed Matrix(S4) Coast Prairie Redox(A16)(LRR K, L,R)
Histic Epipedon(A2) Sandy Redox(S5) Dark Surface(S7)(LRR K,L)
Black Histic(A3) Stripped Matrix(S6) 5 cm Mucky Peat or Peat(S3)(LRR K, L,R)
Hydrogen Sulfide(A4) Loamy Mucky Mineral(F1) Iron-Manganese Masses(F12)(LRR K,L,R)
Stratified Layers(A5) Loamy Gleyed Matrix(F2) Very Shallow Dark Surface(TF12)
2 cm Muck(A10) Depleted Matrix(F3) Other(explain in remarks)
Depleted Below Dark Surface(A11) Redox Dark Surface(F6)
X Thick Dark Surface(Al2) Depleted Dark Surface(F7) 'Indicators of hydrophytic vegetation and weltand
Sandy Mucky Mineral(S1) Redox Depressions(F8) hydrology must be present, unless disturbed or
5 cm Mucky Peat or Peat(S3) problematic
Restrictive Layer�if observed):
Type: Hydric soil present? Y
Depth (inches):
Remarks:
HYDROLOGY
Wetland Hydrology Indicators:
Primarv Indicators(minimum of one is required; check all that applv) Secondarv Indicators(minimum of two re uired
Surface Water(A1) Aquatic Fauna(813) Surface Soil Cracks(B6)
High Water Table(A2) True Aquatic Plants(614) Drainage Patterns(B10)
Saturation(A3) Hydrogen Sulfide Odor(C1) Dry-Season Water Table(C2)
Water Marks(B1) Oxidized Rhizospheres on Living Roots Crayfish Burrows(C8)
Sediment Deposits(B2) (C3) Saturation Visible on Aerial Imagery(C9)
Drift Deposits(B3) Presence of Reduced Iron(C4) Stunted or Stressed Plants(D1)
Algal Mat or Crust(64) Recent Iron Reduction in Tilled Soils X Geomorphic Position(D2)
Iron Deposits(65) (C6) X FAC-Neutral Test(D5)
Inundation Visible on Aerial Imagery(67) Thin Muck Surface(C7)
Sparsely Vegetated Concave Surface(B8) Gauge or Welt Data(D9)
Water-Stained Leaves(B9) Other(Explain in Remarks)
Field Observations:
Surface water present? Yes No X Depth (inches): Wetland
Water table present? Yes No X Depth(inches): hydrology
Saturation present? Yes No X Depth(inches): present? Y
(includes capillary fringe)
Describe recorded data(stream gauge, monitoring well, aerial photos, previous inspections), if available:
Remarks:
US Army Corps of Engineers Midwest Region
WETLAND DETERMINATION DATA FORM -Midwest Region
ProjecUSite 4565 Bayside Rd City/County: Orono/Hennepin Sampling Date: 9-13-14
ApplicanUOwner: Peter and Sharon Rennebohn State: MN Sampling Point: SP 2-1 Up
Investigator(s): FJS, DR 3ection,Township, Range: T117N R23W S06
Landform(hillslope,terrace, etc.): hillslope Local relief(concave, convex, none): none
Slope(%): 3-5 Lat: Long: Datum: NAD83
Soil Map Unit NameAngus-Kilkenny complex, 2 to 6 percent slopes VWI Classification: None
Are climatic/hydrologic conditions of the site typical for this time of the year? N (If no,explain in remarks)
Are vegetation , soil , or hydrology significantly disturbed? Are"normal circumstances"
Are vegetation , soil , or hydrology naturally problematic? present? Yes
SUMMARY OF FINDINGS (If needed,explain any answers in remarks.)
Hydrophytic vegetation present? N
Hydric soil present? Y Is the sampled area within a wetlam N
Wetland hydrology present? N f yes, optional wetland site ID:
Remarks: (Explain alternative procedures here or in a separate report.)
Precipitation for week ending 9/14/2014 was 7.67"above normal since 4/01/2014,1.27"below normal for the preceding 4 weeks and 0..54"below
normal for the preceding week as measured at MSP and reported by the National Agricultural Statistics Service. Precipitation has been erratic in
2014-first extraordinaril wet and now relativel d .Therefore the climatic conditions were recorded as"No".
VEGETATION -- Use scientific names of plants.
Absolute Dominan Indicator pominance Test Worksheet
Tree Stratum (Plot size: 30' ) %Cover t Species Staus Number of Dominant Species
1 that are OBL,FACW,or FAC: 1 (A)
2 Total Number of Dominant
3 Species Across all Strata: 2 (B)
4 Percent of Dominant Species
5 that are OBL, FACW, or FAC: 50.00% (A/B)
0 =Total Cover
Saqlinq/Shrub straturr (Plot size: 15' ) Prevalence Index Worksheet
1 Pinus strobus 3 FACU Total%Cover of:
2 OBL species 0 x 1 = 0
3 FACW species 40 x 2= 80
4 FAC species 0 x 3= 0
5 FACU species 43 x 4= 172
3 =Total Cover UPL species 20 x 5= 100
Herb stratum (Plot size: 5' ) Column totals 103 (A) 352 (B)
1 Solidago canadensis 40 Y FACU Prevalence Index=B/A= 3.42
2 Phalaris arundinacea 40 Y FACW
3 Convolvulus arvensis 10 N UPL Hydrophytic Vegetation Indicators:
4 Asclepias syriaca 10 N UPL Rapid test for hydrophytic vegetation
5 Dominance test is>50%
6 Prevalence index is<_3.0`
� Morphogical adaptations`(provide
$ supporting data in Remarks or on a
g separate sheet)
10 Problematic hydrophytic vegetation`
100 =Total Cover (explain)
Woodv vine stratum (PIOt SIZ@: 30� ) *Indicators of hydric soil and wetland hydrology must be
1 present,unless disturbed or problematic
2 Hydrophytic
0 =Total Cover �egetation
present? N
Remarks: (Include photo numbers here or on a separate sheet)
US Amy Corps of Engineers Midwest Region
SOIL Sampling Point: SP 2-1 Up
Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of indicators.)
Depth Matrix Redox Features
(Inches) Color(moist) % Color(moist) % Type* Loc" Texture Remarks
0-4 10YR 3/2 100 loam High OM, unmasked sand grai
4-6 10YR 3/2 95 10YR 6/4 5 C PL loam
6-12 10YR 3/2 70 10YR 6/4 30 C PL/M clay loam redox in soft masses
12-18 10YR 2/1 100 clay loam
18-30 10YR 3/2 20 10YR 7/1 30 D M loam clay
18-30 10YR 2/1 10 10YR 5/1 30 D M loam clay
18-30 10YR 6/6 10 C PL/M loam clay redox in soft masses
*Type: C=Concentration, D= Depletion, RM= Reduced Matrix, MS= Masked Sand Grains. "Location: PL= Pore Lining, M= Matrix
Hydric Soil Indicators: Indicators for Problematic Hydric Soils:
Histisol(A1) Sandy Gleyed Matrix(S4) Coast Prairie Redox(A16)(LRR K,L, R)
Histic Epipedon (A2) Sandy Redox(S5) Dark Surface(S7)(LRR K,L)
Black Histic(A3) Stripped Matrix(S6) 5 cm Mucky Peat or Peat(S3)(LRR K,L,R)
Hydrogen Sulfide(A4) Loamy Mucky Mineral(F1) Iron-Manganese Masses(F12)(LRR K,L, R)
Stratified Layers(A5) Loamy Gleyed Matrix(F2) Very Shallow Dark Surface(TF12)
2 cm Muck(A10) Depleted Matrix(F3) Other(explain 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) X Redox Depressions(F8) hydrology must be present, unless disturbed or
5 cm Mucky Peat or Peat(S3) problematic
Restrictive Layer(if observed):
Type: Hydric soil present? Y
Depth(inches):
Remarks:
HYDROLOGY
Wetland Hydrology Indicators:
Primarv Indicators(minimum of one is reauired� check all that applvl Secondar Indicators minimum of two re uired
Surface Water(A1) Aquatic Fauna(613) Surface Soil Cracks(B6)
High Water Table(A2) True Aquatic Plants(B14) Drainage Patterns(B10)
Saturation(A3) Hydrogen Sulfide Odor(C1) Dry-Season Water Table(C2)
Water Marks(61) Oxidized Rhizospheres on Living Roots Crayfish Burrows(C8)
Sediment Deposits(62) (C3) Saturation Visible on Aerial Imagery(C9)
Drift Deposits(B3) Presence of Reduced Iron(C4) Stunted or Stressed Plants(D1)
Algal Mat or Crust(64) Recent Iron Reduction in Tilled Soils Geomorphic Position(D2)
Iron Deposits(B5) (C6) _FAC-Neutral Test(D5)
Inundation Visible on Aerial Imagery(87) Thin Muck Surface(C7)
Sparsely Vegetated Concave Surface(68) Gauge or Well Data(D9)
Water-Stained Leaves(69) Other(Explain in Remarks)
Field Observations:
Surface water present? Yes No X Depth(inches): Wetland
Water table present? Yes No X Depth (inches): hydrology
Saturation present? Yes No X Depth(inches): present? N
(includes capillary fringe)
Describe recorded data(stream gauge, monitoring well, aerial photos, previous inspections), if available:
Remarks:
US Army Corps of Engineers Midwest Region
WETLAND DETERMINATION DATA FORM - Midwest Region
ProjecUSite 4565 Bayside Rd City/County: Orono/Hennepin Sampling Date: 9-13-14
ApplicanUOwner: Peter And Sharon Rennebohn State: MN Sampling Point: SP 2-1 Wet
Investigator(s): FJS, DR 3ection,Township, Range: T117N R23W S06
Landform (hillslope,terrace, etc.): Depression Local relief(concave, convex, none): Concave
Slope(%): 0 Lat: Long: Datum: NAD83
Soil Map Unit NameAngus-Kilkenny complex, 2 to 6 percent slopes VWI Classification: None
Are climatic/hydrologic conditions of the site typical for this time of the year? N (If no, explain in remarks)
Are vegetation ,soil , or hydrology significantly disturbed? Are"normal circumstances"
Are vegetation ,soil , or hydrology naturally problematic? present? Yes
SUMMARY OF FINDINGS (If needed,explain any answers in remarks.)
Hydrophytic vegetation present? Y
Hydric soil present? Y Is the sampled area within a wetlan� Y
Wetland hydrology present? Y f yes, optional wetland site ID:
Remarks: (Explain alternative procedures here or in a separate report.)
Precipitation for week ending 9/14/2014 was 7.67"above normal since 4/01/2014,1.27"below normal for the preceding 4 weeks and 0..54"below
normal for the preceding week as measured at MSP and reported by the National Agricultural Statistics Service. Precipitation has been erratic in
2014-first extraordinaril wet and now relativel d .Therefore the climatic conditions were recorded as"No".
VEGETATION -- Use scientific names of plants.
Absolute Dominan Indicator pominance Test Worksheet
Tree Stratum (Plot size: 30' ) %Cover t Species Staus Number of Dominant Species
� that are OBL, FACW,or FAC: 1 (A)
2 Total Number of Dominant
3 Species Across all Strata: 1 (B)
4 Percent of Dominant Species
5 that are OBL, FACW,or FAC: 100.00% (A/B)
0 =Total Cover
Saplina/Shrub straturr (Plot size: 15' ) Prevalence Index Worksheet
� Total%Cover of:
2 OBL species 0 x 1 = 0
3 FACW species 100 x 2= 200
4 FAC species 0 x 3= 0
5 FACU species 0 x 4= 0
0 =Total Cover UPL species 0 x 5= 0
Herb stratum (Plot size: 5' ) Column totals 100 (A) 200 (B)
1 Phalaris arundinacea 100 Y FACW Prevalence Index= B/A= 2.00
2
3 Hydrophytic Vegetation Indicators:
4 Rapid test for hydrophytic vegetation
5 X Dominance test is>50%
g X Prevalence index is<_3.0`
7 Morphogical adaptations*(provide
8 supporting data in Remarks or on a
g separate sheet)
10 Problematic hydrophytic vegetation`
100 =Total Cover (explain)
WOOdV Vlne StfBtUm (PIOt SizB: 30' ) *Indicators of hydric soil and wetland hydrology must be
� present,unless disturbed or problematic
2 Hydrophytic
0 =Total Cover vegetation
present? Y
Remarks: (Include photo numbers here or on a separate sheet)
US Amy Corps of Engineers Midwest Region
SOIL Sampling Point: SP 2-1 Wet
Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of indicators.)
Depth Matrix Redox Features
(Inches) Color(moist) % Color(moist) % Type' Loc"` Texture Remarks
0-4 10YR 3/1 100 loam High OM
4-10 10YR 3/1 90 10YR 5/2 10 D PL loam
10-17 10YR 5/1 70 10YR 3/1 30 M loam clay
17-20 10YR 4/1 50 10YR 6/3 20 C M loam clay
17-20 10YR 3/1 30 loam clay
20-30 10YR 6/3 50 10YR 4/1 20 D M loam clay
20-30 10YR 3/1 30 loam clay
*Type: C=Concentration, D= Depletion, RM= Reduced Matrix, MS= Masked Sand Grains. **Location: PL= Pore Lining, M= Matrix
Hydric Soil Indicators: Indicators for Problematic Hydric Soils:
Histisol(A1) Sandy Gleyed Matrix(S4) Coast Prairie Redox(A16)(LRR K,L, R)
Histic Epipedon(A2) Sandy Redox(S5) Dark Surface(S7)(LRR K,L)
Black Histic(A3) Stripped Matrix(S6) 5 cm Mucky Peat or Peat(S3)(LRR K,L,R)
Hydrogen Sulfide(A4) Loamy Mucky Mineral(F1) Iron-Manganese Masses(F12)(LRR K,L, R)
Stratified Layers(A5) Loamy Gleyed Matrix(F2) Very Shallow Dark Surface(TF12)
2 cm Muck(A10) Depleted Matrix(F3) Other(explain in remarks)
X Depleted Below Dark Surface(A11) Redox Dark Surface(F6)
Thick Dark Surface(Al2) X Depleted Dark Surface(F7) *Indicators of hydrophytic vegetation and weltand
Sandy Mucky Mineral(S1) Redox Depressions(F8) hydrology must be present, unless disturbed or
5 cm Mucky Peat or Peat(S3) problematic
Restrictive Layer(if observed):
Type: Hydric soil present? Y
Depth(inches):
Remarks:
HYDROLOGY
Wetland Hydrology Indicators:
Primarv Indicators(minimum of one is required check all that applv) Secondar Indicators minimum of two re uired
Surface Water(A1) Aquatic Fauna(613) Surface Soil Cracks(B6)
High Water Table(A2) True Aquatic Plants(614) Drainage Patterns(610)
Saturation(A3) Hydrogen Sulfide Odor(C1) Dry-Season Water Table(C2)
Water Marks(B1) Oxidized Rhizospheres on Living Roots Crayfish Burrows(C8)
Sediment Deposits(62) (C3) Saturation Visible on Aerial Imagery(C9)
Drift Deposits(B3) Presence of Reduced Iron(C4) Stunted or Stressed Plants(D1)
Algal Mat or Crust(64) Recent Iron Reduction in Tilled Soils X Geomorphic Position(D2)
Iron Deposits(B5) (C6) X FAC-Neutral Test(D5)
Inundation Visible on Aerial Imagery(B7) Thin Muck Surface(C7)
Sparsely Vegetated Concave Surface(68) Gauge or Well Data(D9)
Water-Stained Leaves(69) Other(Explain in Remarks)
Field Observations:
Surface water present? Yes No X Depth(inches): Wetland
Water table present? Yes No X Depth (inches): hydrology
Saturation present? Yes No X Depth (inches): present? Y
(includes capillary fringe)
Describe recorded data(stream gauge, monitoring well, aerial photos, previous inspections), if available:
Remarks:
US Army Corps of Engineers Midwest Region
THE TECHNICAL DOCUMENTATION SECTION
Plant Indicator Status
INDICATOR CATEGORIES*
Obligate Wetland (OBL)—Occur almost always (estimated probability >99%) under natural
conditions in wetlands.
Facultative Wetland (FACW)—Usually occur in wetlands (estimated probability 67% - 99%),
but occasionally found in non-wetlands.
Facultative (FAC)—Equally likely to occur in wetlands or non-wetlands (estimated probability
34% - 66%).
Facultative Upland (FACU) —Usually occur in non-wetlands (estimated probability 67% -
99%), but occasionally found in wetlands (estimated probability 1% -33%).
Obligate Upland (UPL)—Occur in wetlands in another region, but occur almost always
(estimated probabiliry >99%) under natural conditions in non-wetlands in the region specified. If
a species does not occur in wetlands in any region, it is not on the National List.
*Reed, P.B. 1988. National list of plant species that occur in wetlands: Minnesota. National
Wetlands Inventory, U.S. Fish and Wildlife Service, St. Petersburg, Florida.
THE TECHNICAL DOCUMENTATION SECTION
Soil Series Descriptions
Acquired from Natural Resource Conservation Service Website, Official Soil Series Descriptions
ANGUS SERIES
The Angus series consists of very deep, well drained soils formed in calcareous loamy glacial till on
moraines and till plains. Permeability is moderate. Slopes range from 2 to 5 percent. Mean annual
precipitation is about 28 inches. Mean annual air temperature is about 46 degrees F.
TAXONOMIC CLASS: Fine-loamy, mixed, superactive, mesic Mollic Hapludalfs
TYPICAL PEDON: Angus loam with a convex slope of about 5 percent on a ground
moraine in a cultivated field. (Colors are for moist soil unless otherwise noted.)
Ap--O to 8 inches; black(lOYR 2/1) loam, dark grayish brown (lOYR 4/2) dry; weak fine
granular structure; friable; many very fine roots; about 2 percent gravel; neutral; abrupt
smooth boundary. (6 to 10 inches thick)
Btl--8 to 23 inches; dark yellowish brown (lOYR 4/4) 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 gravel; slightly acid; gradual wavy
boundary.
Bt2--23 to 35 inches; brown(lOYR 4/3) clay loam; moderate medium subangular blocky
structure; firm; common faint very dark grayish brown (lOYR 3/2) clay films on faces of
peds and root channels; common very fine roots; about 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; weak medium subangular blocky
structure; friable; few faint brown (lOYR 4/3) clay films in root channels; about 4 percent
gravel; slightly effervescent; slightly alkaline; gradual wavy boundary. (0 to 12 inches
thick)
C--40 to 80 inches; brown (lOYR 5/3) loam; massive; friable; common fine distinct
grayish brown (2.SY 5/2) Fe depletion and common medium distinct yellowish brown
(lOYR 5/6) Fe concentrations; about 7 percent gravel; strongly effervescent; slightly
alkaline.
TYPE LOCATION: Wright County, Minnesota; about 1 mile south of Montrose, 200
feet north and 80 feet east of the southwest corner of sec. 1, T. 118 N., R. 26 W.; USGS
Waverly quadrangle; lat. 45 degrees 03 minutes 20 seconds N.; long. 93 degrees 54
minutes 38 seconds W., NAD27.
RANGE IN CHARACTERISTICS: Depth to free calcium carbonates ranges from 24
to 54 inches. Rock fragments of mixed lithology comprise 2 to 8 percent of the volume
throughout. Soil saturation occurs in the lower third of the series control section for
periods of one month or more. These soils are dry for more than 60 days in the soil
moisture control section during the 120 days following the summer solstice. The clay
content ranges from 22 to 30 percent and the sand content 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 loam and fine sandy loam are within the
range. The reaction is moderately acid to neutral.
Some pedons have a E horizon with hue of lOYR, value of 4 or 5, and chroma of 1 to 3.
It is loam, sandy loam or fine sandy loam. The reaction is moderately acid to neutral.
The Bt horizon has hue of lOYR or 2.SY, value of 4 or 5, and chroma of 3 or 4. It is clay
loam, loam, or sandy clay loam. Redoximorphic features are present in the lower part of
the Bt horizon in some pedons. The B/A clay ratios range from 1.2 to 1.4 . It is strongly
acid to slightly acid in the upper part and moderately acid to neutral in the lower part.
A Bk horizon is present in some pedons.
The BC horizon has soil color and textures similar to the Bt and C horizon respectively.
Clay films are on ped faces or root channels. The reaction is slightly acid to slightly
alkaline.
The C horizon has hue of 2.SY or lOYR, value of 4 to 6 and chroma of 3 to 5. It is loam
or clay loam. It is slightly alkaline or moderately alkaline. Redox depletions with chroma
of 2 or less are in this horizon.
COMPETING SERIES: These are the Argyle, Baltimore, Bassett, Bloomin�, Caleb,
Dowagiac, Dunbrid�e, Gara, Koronis, Lauramie, Lester, Lon�lois, Lvdick, Mohawk,
Neda, Newcomer, Oneco, Orwood, Racine, Razort, Sebbo, Taopi, Waucoma, and
Winneshiek soils. The Argyle, Baltimore, Blooming, Gara Koronis, Lester, Lydick,
Mohawk, Razort and Taopi soils do not have soil saturation in the lower third of the
series control section for more than 1 consecutive month. The Bassett, Caleb, Orwood,
and Sebbo soils do not have free carbonates above a depth of 48 inches. Dowagiac soils
have sandy outwash sediments with less than 10 percent clay in the lower third of the
series control section. Dunbridge and Winneshiek soils have sola terminated by limestone
bedrock at depths of 20 to 40 inches. Lauramie soils are dry in some parts of the soil
moisture control section for less than 60 days during the 120 days following the summer
solstice. Longlois soils have 15 to 60 percent rock fragments in the lower half of the
series control section. Neda and Racine soils have less than 30 percent sand in the upper
one fourth of the series control section. Newcomer, Oneco and Waucoma soils have sola
terminated by a lithic contact at depths of 40 to 60 inches.
GEOGRAPHIC SETTING: These soils have convex slopes on moraines or till plains.
Slopes range from 2 to 5 percent. They formed in calcareous, 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. Frost-free days range from 125 to 165.
Elevation above sea level ranges from 700 to 1600 feet.
GEOGRAPHICALLY ASSOCIATED SOILS: These includes the Cordova, Dundas,
Glencoe, Hamel, Hou�hton, Klossner, and Le Sueur soils which formed in similar parent
materials. Poorly drained Cordova and Dundas soils are 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. Very poorly drained Houghton and
Klossner soils are organic and are in depressions. Moderately well drained Le Sueur soils
are on slightly elevated flats and less sloping area.
DRAINAGE AND PERMEABILITY: Well drained. 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 corn and soybeans. Native vegetation is
mixed prairie grasses and deciduous forest.
DISTRIBUTION AND EXTENT: South-central and east-central Minnesota and
possibly northeastern Iowa. Moderate extent. MLRA-103.
MLRA OFFICE RESPONSIBLE: St. Paul, Minnesota
SERIES ESTABLISHED: Meeker County, Minnesota, 1995.
REMARKS: Diagnostic horizons and features recognized in this pedon are: mollic
subgroup - the zone from the surface to a depth of 8 inches (Ap horizon); argillic horizon
- the zone from 8 to 35 inches (Bt horizons); This soil was previously included in the
Lester series. However, due to more investigations, it was concluded that Lester soils on
a slope of 2 to 5 percent have seasonal high water table between 3.5 and 6 feet rather than
6 feet or greater.
ADDITIONAL DATA: Soil Interpretation Record number MN0830.
KILKENNY SERIE S
The Kilkenny series consists of very deep, moderately well drained soils that formed in a
mantle of clayey glacial till or flow till and underlying loamy glacial till on moraines.
These soils have moderately slow permeability. Their slopes range from 2 to 35 percent.
The mean annual precipitation is about 28 inches. Mean annual air temperature is about
48 degrees F.
TAXONOMIC CLASS: Fine, smectitic, mesic Oxyaquic Vertic Hapludalfs
TYPICAL PEDON: Kilkenny clay loam with a 15 percent linear sideslope on a glacial
moraine in a pastured field. (Colors are for moist soil 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; common very fine roots; about 2 percent
gravel; moderately acid (pH 5.6); abrupt smooth boundayr. (6 to 10 inches thick)
Btl--9 to 19 inches; brown(lOYR 4/3) silty clay loam; moderately medium subangular
blocky structure parting to moderately fine subangular 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 boundary.
Bt2--19 to 38 inches; brown (lOYR 4/3) clay loam; moderate medium prismatic structure
parting to moderate medium subangular blocky; firm; common very fine roots; common
distinct very dark brown (lOYR 2/2) clay films on faces of peds; about 5 percent gravel;
strongly acid; gradual wavy boundary.
Bt3--38 to 53 inches; brown (lOYR 4/3) clay loam; weak medium subangular blocky
structure parting to weak fine subangular blocky; firm; common distict very dark brown
(lOYR 2/2) clay films on faces of peds; about 5 percent gravel; few fine distict brown
(7.SYR 4/4) Fe concentrations; moderately acid; gradual 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) loam; weak fine subangular blocky
structure; few distinct dark brown (lOYR 3/3) clay films on faces of peds; friable; about 8
percent gravel; about 2 percent cobbles; few fine distinct brown (7.SYR 4/4) Fe deletions;
slightly effervescent; slightly alkaline; gradual wavy boundary.
2C--65 to 80 inches; light olive brown (2.SY 5/4) loam; massive; friable; few
concentrations of light gray (2.SY 7/2) calcium carbonates in pores; brown (7.SYR 4/4)
soft masses of iron-manganese in nodules; about 8 percent gravel; about 2 percent
cobbles; common medium prominent dark yellowish brown (lOYR 4/6) Fe
concentrations and common medium distinct gray (2.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 north of the southwest corner of Sec.
19, T.111N., R.23W.; USGS Montgomery quadrangle; lat. 44 degrees 24 minutes 3
seconds N., and long. 93 degrees 38 minutes 41 seconds W., NAD 27.
RANGE IN CHARACTERISTICS: Depth to free carbonates 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 section, but the upper part of the profile in
some pedons contains less than 2 percent gravel. Rounded shale fragments dominate the
coarse sand fraction. Soil saturation occurs above a depth 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 reaction 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 or 5, and chroma of 3 to 5. Faint to
prominent Fe concentrations and depletions commonly are above a depth of 40 inches.
Redox depletions do not occur in the upper 10 inches of this horizon. The upper 20
inches of the Bt horizon typically contains 35 to 45 percent clay. B/A clay ratios are 1.2
to 1.4. The Bt horizon is clay loam, silty clay loam, or clay. The reaction strongly acid to
neutral.
The 2BC horizon has properties similar to the 2C horizon. Some pedons have a 2BK
horizon.
The 2C horizon has hue of lOYR or 2.SY, value of 4 or 5, and chroma of 2 to 5. It is clay
loam or loam. The reaction is slightly alkaline or moderately alkaline.
COMPETING SERIES: There are no competing series.
GEOGRAPHIC SETTING: Kilkenny soils have plane and convex slopes on gently
sloping to steep end moraines of the Des Moines lobe of the Late Wisconsinan glaciation.
Their slopes range from 2 to 35 percent. They formed in a mantle of clayey glacial till or
flow till and underlying loamy glacial till on moraines. Mean annual temperature ranges
from 45 to 52 degrees F. Mean annual precipitation is about 25 to 32 inches. Frost-free
days range from 145 to 175. Elevation above sea level ranges from 800 to 1500 feet.
GEOGRAPHICALLY ASSOCIATED SOILS: These are the Glencoe, Lerdal, Lester,
Le Sueur, Lura, Mazaska, and Shields series. The very poorly drained Glencoe and Lura
soils are in the lower lying drainageways and depressions. The somewhat poorly drained
Lerdal soils are on gently sloping to moderately steep areas. Shields soils are poorly
drained, and are on slightly elevated flats. Mazaska soils are poorly drained, and are on
slightly elevated flats and swales above or within areas 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: Moderately well drained. Permeability is
moderately slow. Runoff is medium to very high. A perched seasonal high water table
occurs at depths of 2.5 to 4.0 feet during the period April, May, and June in normal years.
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 Minnesota and north-central Iowa. The
series is of moderate extent.
MLRA OFFICE RESPONSIBLE: St. Paul, Minnesota
SERIES ESTABLISHED: Waseca County, Minnesota, 1963.
REMARKS: Diagnostic horizons and features recognized in this pedon are: Ochric
epipedon - the zone from the soil surface to a depth of 9 inches (Ap horizon); Argillic
horizon - the zone from 9 to 53 inches (Btl, Bt2, Bt3 horizons); Oxyaquic subgroup
based on saturation above a depth of 40 inches; Vertic subgroup based on more than 6 cm
of COLE in upper 40 inches. Water table studies and field observations have verified a
perched condition in most years, particularly in periods of extended rainfall.
ADDITIONAL DATA: Soil Interpretation Record number MN0376.
LESTER SERIES
The Lester series consists of very deep, well drained soils that formed in calcareous loamy glacial till on till
plains and moraines. These soils have moderate permeability. Their slopes range from 5 to 70 percent.
Mean annual precipitation is about 28 inches. Mean annual temperature is about 47 degrees F.
TAXONOMIC CLASS: Fine-loamy, mixed, superactive, mesic Mollic Hapludalfs
TYPICAL PEDON: Lester loam with a convex slope of about 9 percent on a ground
moraine in a cultivated field. (Colors are for moist soil unless otherwise noted.)
Ap--O to 7 inches; very dark grayish brown(lOYR 3/2) loam, grayish brown (lOYR 5/2)
dry; moderate fine subangular blocky structure; friable; many fine roots; about 3 percent
gravel; slightly acid; abrupt smooth boundary. (6 to 10 inches thick)
Btl--7 to 21 inches; brown (lOYR 4/3) clay loam; moderate medium subangular blocky
structure; firm; many very fine roots; common very dark grayish brown(lOYR 3/2) clay
films on faces of peds and few very dark gray (lOYR 3/1) organic coats on faces of peds;
about 2 percent gravel; slightly acid; clear smooth boundary.
Bt2--21 to 38 inches; dark yellowish brown (lOYR 4/4) clay loam; moderate medium
subangular blocky structure; friable; common fine roots; common dark grayish brown
(lOYR 4/2) clay films on faces of peds and few very dark brown (lOYR 2/2) organic
coats on faces of peds; about 3 percent gravel; slightly acid; gradual smooth boundary.
(Combined Bt horizon is 10 to 40 inches.)
Bk1--38 to 50 inches; yellowish brown (lOYR 5/4) loam; weak medium subangular
blocky structure; friable; few fine roots; common very pale brown (l 0YR 8/2) carbonate
threads; about 2 percent gravel; violently effervescent; slightly alkaline; clear wavy
boundary.
Bk2--50 to 60 inches; yellowish brown (lOYR 5/4) loam; weak medium subangular
blocky structure; friable; common fine distinct yellowish brown (lOYR 5/6) relict Fe
concentrations; common very pale brown (1 OYR 8/2) carbonate threads; about 2 percent
gravel; violently effervescent; slightly alkaline; clear wavy boundary.
C--60 to 80 inches; yellowish brown (l 0YR 5/4) loam; ; massive; friable; common
medium distinct yellowish brown (lOYR 5/6) relict Fe concentrations and few fine
distinct light brownish gray (lOYR 6/2)relict Fe depletions; about 1 percent gravel;
strongly effervescent; slightly alkaline.
TYPE LOCATION: Wright County, Minnesota; about 3 miles west of Otsego, 1460
feet south and 200 feet west of the northeast corner of Sec. 15, T.121 N., R.24 W.; USGS
Big Lake quadrangle; lat. 45 degrees 17 minutes 29 seconds N.; long. 93 degrees 41
minutes 3 seconds W., NAD27
RANGE IN CHARACTERISTICS: Depth to free carbonates ranges from 20 to 54
inches. Rock fragments of mixed lithology comprise 1 to 8 percent of the volume of the
control section.
The A or Ap horizons have hue of lOYR, value of 2 or 3, and chroma of 1 or 2. The E
horizon where present, has value of 3 to 5, and chroma of 1 to 3. The A and E horizons
are loam or clay loam, but sandy loam, fine sandy loam, or silt loam is within the range.
They range from moderately acid to neutral.
The Bt horizon has hue of lOYR or 2.SY, value of 4 or 5, and chroma of 3 or 4. It is clay
loam or loam and has 24 to 35 percent clay and 30 to 45 percent sand. The B/A clay
ratios range from 1.2 to 1.4. It is strongly acid to slightly acid in the upper part and
moderately acid to neutral in the lower part. A Bw horizon is sometimes present below
the Bt.
The Bk horizon has hue of lOYR or 2.SYR, value of 4 or 5, and chroma of 3 to 6. The Bk
horizon is loam or clay loam. It is slightly alkaline or moderately alkaline. Relict
redoximorphic features are present in some pedons.
The C horizon has hue of 2.SY or lOYR, value of 4 to 6, and chroma of 3 to 6. It is loam
or clay loam. It is slightly alkaline or moderately alkaline. Relict redoximorphic features
are present in some pedons.
COMPETING SERIES: These are the Angus, Ar�yle, Baltimore, Bassett, Bloomin�,
Caleb, Dowagiac, Dunbrid�e, Gara, Koronis, Lauramie, Lon�lois, Lydick, Mohawk,
Neda, Newcomer, Oneco, Orwood, Racine, Razort, Sebbo, Taopi, Waucoma, and
Winneshiek soils in the same family. Angus and Sebbo soil have saturation in the lower
third of the series control section. Argyle, Baltimore, and Oneco soils have B horizons
with 7.SYR or redder hue. Bassett soils are very strongly acid to moderately acid in the
upper part of the Bt horizon. Blooming and Racine soils have 15 to 35 percent sand in the
upper part of the particle-size control section. Caleb soils have some subhorizons that
have more than 45 percent in the lower part of the control section. Dowagiac and Koronis
soils have less than 24 percent clay in the lower one third of the particle-size control
section. Dunbridge, Waucoma,Newcomer and Winneshiek soils have sola terminated by
bedrock at depths above 60 inches. Gara soils average less than 2 percent rock fragments
in the control section. Longlois, Lydic, and Neda soils have more than 8 percent rock
fragments in some subhorizon of the control section. Lauramie soils have more than 45
percent sand in some subhorizon in the middle part of the control section. Mohawk soils
have a higher content of silt and have dark colors in the B horizon which apparently are
inherited from dark shale. Orwood soils have no rock fragments in the particle-size
control section. Razort soils have less than 30 percent sand in the control section.
GEOGRAPHIC SETTING: These soils have convex slopes on moraines and till plains.
Slope gradients range from 5 to 70 percent. They formed in calcareous, loamy glacial till
of late Wisconsinan Age. Mean annual temperature ranges from 45 degrees to 52 degrees
F. Mean annual precipitation ranges from 25 to 33 inches. Frost free days range from 125
to 165. Elevations range from 700 to 1600 feet.
GEOGRAPHICALLY ASSOCIATED SOILS: These include the Cordova, Dundas,
Glencoe, Hamel, Hou�hton, Klossner, Le Sueur, Muske�o, and Nessel soils. Poorly
drained Cordova and somewhat poorly and poorly drained Dundas soils are on flats and
upper drainageways with a high seasonal water table. Very poorly drained Glencoe,
Houghton, Klossner, and Muskego soils are mostly in depressions. Poorly drained Hamel
soils are on foot and toe slopes. Moderately well drained Le Sueur and Nessel soils are on
slightly elevated flats and gently convex slopes.
DRAINAGE AND PERMEABILITY: Well drained. Permeability is moderate. Runoff
is medium to high.
USE AND VEGETATION: Mostly cropped to corn and soybeans. Some is in pasture
and forest. Native vegetation is savanna.
DISTRIBUTION AND EXTENT: South-central and east-central Minnesota and
northeastern Iowa. Extensive.
MLRA OFFICE RESPONSIBLE: St. Paul, Minnesota
SERIES ESTABLISHED: Dakota County, Minnesota, 1945.
REMARKS: Diagnostic horizons and featured recognized in this pedon are: mollic
subgroup - the zone from the surface to 7 inches (Ap horizon); argillic horizon - the zone
from 7 to 38 inches (Bt horizons). Type location moved from Waseca County, Mn. to
Wright County, Mn., 11/96 to better exemplify the series concept within the MLRA.
Slopes of 1 to 5 percent that were previously correlated as Lester may be included with
the Angus series in the future.
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Wetland 1 — IMG_1739 View of wetland sample point at transect SP 1-1, pink in
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Wetland 2 — IMG_1749 View of wetland sample point at transect SP 2-1, pink
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Project Name and/or Number: SER#2014-022-03—4565 Bayside Road,Orono
PART ONE: Applicant Information
If applicant is an entity(company,government entity, partnership, etc.),an authorized contact person must be identified. If the
applicant is using an agent(consultant, lawyer, or other third party)and has authorized them to act on their behalf,the agent's
contact information must also be provided.
Applicant/Landowner Name: peter & Sharon Rennebohn
Mailing Address: 4565 Bayside Road, Maple Plain, MN 55359
Phone: 952-472-7369
E-mail Address: prennebohn@msn.com
Authorized Contact(do not complete if same as above): Frank Svoboda—Svoboda Ecological Resources
Mailing Address: 22752 Co Rd 7, Hutchinson, MN 55350
Phone: 612-384-7770
E-mail Address: franks@gpsinnovatitons.com
PART TWO: Site Location Information
County: Hennepin City/Township: Orono
Parcel ID and/or Address: 4565 Bayside ROad(PID#06-117-23-21-0005)
Legal Description(Section,Township,ttange): A part of the NW '/a NE 1/4 NW `/a, Section 6, T 117N, R23 W, (
of Orono, Hennepin County, Minnesota
Lat/Long(decimal degrees): Lat.44.977683(44°58'39.6588"N)/Long.-93.639104(93°38'20.7744"W)
Attach a map showing the location of the site in relation to local streets, roads,highways.
.��� -- .. �- ; �������' � �� �
._: ��
I.ghborhood �. ;� ����� , ns� '"y�f+� ��r �d�,, � � � .�.�j
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.��S ,a� �'1 , ati c ySi.' w.�` :e�
Approximate size of site ;acres)or if a linear project, ._ a_ . ,:L_:; �:�*�;-�_s
If you know that your proposal will require an individual Permit from the U.S.Army Corps of Engineers,you must provide the
names and addresses of all property owners adjacent to the project site. This information may be provided by attaching a list to
your application or by using block 25 of the Application for Department of the Army permit which can be obtained at:
http://www.mvp.usace.army.mil/Portals/57/docs/resulatorv/RegulatoryDocs/en�form 4345 2012oct.pdf
Project Name and/or Number: SER#2014-022-03—4565 Bayside Road,Orono
PART THREE: General Project/Site Information
If this application is related to a delineation approval, exemption determination,jurisdictional determination,or other
correspondence submitted prior to this application then describe that here and provide the Corps of Engineers project number.
Describe the project that is being proposed,the project purpose and need,and schedule for implementation and completion.The
project description must fully describe the nature and scope of the proposed activity including a description of all project elements
that effect aquatic resources(wetland, lake,tributary,etc.)and must also include plans and cross section or profile drawings
showing the location, character, and dimensions of all proposed activities and aquatic resource impacts.
The owner wants to know where the approved edge is located before starting the planning process.As soon as approval is
received they will move forward with their project.
PART FOUR: Aquatic Resource Impact1 Summary
If your proposed project involves a direct or indirect impact to an aquatic resource (wetland, lake, tributary, etc.) identify each
impact in the table below. Include all anticipated impacts, including those expected to be temporary. Attach an overhead view
map, aerial photo, and/or drawing showing all of the aquatic resources in the project area and the location(s) of the proposed
impacts. Label each aquatic resource on the map with a reference number or letter and identify the impacts in the following table.
Aquatic Type of Impact Duration of Existing Plant County,Major
Aquatic Resource Overall Size of Watershed#,
Resource Type (fill,excavate, Impact z Community
ID(as noted on Size of Impact Aquatic and Bank Service
(wetland,lake, drain,or remove Permanent(P)or 3 Type(s)in Impac
overhead view) 1 Resource 4 Area#of Impact
tributary etc.) vegetation) Temporary(T) Area 5
Area
llf impacts are temporary;enter the duration of the impacts in days next to the"T". For example,a project with a temporary access fill that would be removed
after 220 days would be entered"T(220)".
Zlmpacts less than 0.01 acre should be reported in square feet. Impacts 0.01 acre or greater should be reported as acres and rounded to the nearest 0.01 acre.
Tributary impacts must be reported in linear feet of impact and an area of impact by indicating first the linear feet of impact along the flowline of the stream
followed by the area impact in parentheses). For example,a project that impacts 50 feet of a stream that is 6 feet wide would be reported as 50 ft(300 sq/ft).
3This is generally only applicable if you are applying for a de minimis exemption under MN Rules 8420.0420 Subp.8,otherwise enter"N/A".
°Use Wetland Plants and Plant Community Types of Minnesota ond Wisconsin 3''Ed.as modified in MN Rules 8420.0405 Subp.2.
SRefer to Major Watershed and Bank Service Area maps in MN Rules 8420.0522 Subp.7.
If any of the above identified impacts have already occurred, identify which impacts they are and the circumstances associated
with each:
PART FIVE: Applicant Signature
❑ Check here if you are requesting a pre-application consultation with the Corps and LGU based on the information you have
provided. Regulatory entities will not initiate a formal application review if this box is checked.
By signature below, I attest that the information in this application is complete and accurate. I further attest that I possess the
authority to undertake the work described herein.
Signature: `� —A � d Date: September 22, 2014
I hereby authorize Svoboda Ecological Resources to act on my behalf as my agent in the processing of this application and to
furnish, upon request,supplemental information in support of this application.
1 The term"impact"as used in this joint application form is a generic term used for disclosure purposes to identify
activities that may require approval from one or more regulatory agencies. For purposes of this form it is not meant to
indicate whether or not those activities may require mitigation/replacement.
Project Name and/or Number: SER#2014-022-03—4565 Bayside Road,Orono
' Attachment A
Request for Delineation Review, Wetland Type Determination, or
� Jurisdictional Determination
By submission of the enclosed wetland delineation report, I am requesting that the U.S.Army Corps of Engineers,St. Paul District
(Corps)and/or the Wetland Conservation Act Local Government Unit(LGU) provide me with the following(check all that apply):
�Wetland Type Confirmation
QDelineation Concurrence. Concurrence with a delineation is a written notification from the Corps and a decision from the LGU
concurring, not concurring,or commenting on the boundaries of the aquatic resources delineated on the property. Delineation
concurrences are generally valid for five years unless site conditions change. Under this request alone,the Corps will not address
the jurisdictional status of the aquatic resources on the property, only the boundaries of the resources within the review area
(including wetlands,tributaries, lakes,etc.).
QPreliminary Jurisdictional Determination.A preliminary jurisdictional determination (PJD) is a non-binding written indication
from the Corps that waters, including wetlands, identified on a parcel may be waters of the United States. For purposes of
computation of impacts and compensatory mitigation requirements,a permit decision made on the basis of a PJD will treat all
waters and wetlands in the review area as if they are jurisdictional waters of the U.S. PJDs are advisory in nature and may not be
appealed.
❑Approved Jurisdictional Determination.An approved jurisdictional determination (AJD)is an official Corps determination that
jurisdictional waters of the United States are either present or absent on the property.AJDs can generally be relied upon by the
affected party for five years.An AlD may be appealed through the Corps administrative appeal process.
In order for the Corps and LGU to process your request,the wetland delineation must be prepared in accordance with the 1987
Corps of Engineers Wetland Delineation Manual,any approved Regional Supplements to the 1987 Manual, and the Guidelines for
Submitting Wetland Delineations in Minnesota(2013).
http://www.mvp.usace.army.mil/Missions/Re�ulatorv/DelineationJDGuidance.aspx
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Project Name and/or Number: SER#2014-031-03–225 Old Crystal Bay Rd N,Orono
PART ONE: Applicant Information
If applicant is an entity(company,government entity, partnership,etc.),an authorized contact person must be identified. If the
applicant is using an agent(consultant, lawyer,or other third party)and has authorized them to act on their behalf,the agent's
contact information must also be provided.
Applicant/Landowner Name: Sherry Underdahl
MailingAddress: 400 Ranchview Lane, Plymouth, MN 55446
Phone: 763-383-5586
E-mail Address: junderd@iphouse.com
Authorized Contact(do not complete if same as above): Frank Svoboda–Svoboda Ecological Resources
MailingAddress: 22752 Co Rd 7, Hutchinson, MN 55350
Phone: 612-384-7770
E-mail Address: franks@gpsinnovatitons.com
PART TWO: Site Location Information
County: Hennepin City/Township: Orono
Parcel ID and/or Address: 225 Old Crystal Bay Road N (PID#331 1823310007)
Legal Description(Section,Township, Range): S 1/3 NE '/4 SW '/4 Section 33, T118N, R23W, City of
Orono, Hennepin County, Minnesota
Lat/Long(decimal degrees): Lat.44.975994(44°58'33.5784"N)/Long.-93.594274(93°35'39.3864"W)
Attach a map showing the location of the site in relation to local streets, roads,highways.
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Approximate size of site(acres)or if a linear project, length(feet): 5.2 Acres
If you know that your proposal will require an individual Permit from the U.S.Army Corps of Engineers,you must provide the
names and addresses of all property owners adjacent to the project site. This information may be provided by attaching a list to
your application or by using block 25 of the Application for Department of the Army permit which can be obtained at:
http://www.mvp.usace.armv.mil/Portals/57/docs/re�ulatorv/Re�ulatorvDocs/en�form 4345 2012oct.pdf
Project Name and/or Number: SER#2014-031-03—225 Old Crystal Bay Road N,Orono
PART THREE: General Project/Site Information
If this application is related to a delineation approval, exemption determination,jurisdictional determination,or other
correspondence submitted prior to this application then describe that here and provide the Corps of Engineers project number.
Describe the project that is being proposed,the project purpose and need, and schedule for implementation and completion.The
project description must fully describe the nature and scope of the proposed activity including a description of all project elements
that effect aquatic resources(wetland, lake,tributary,etc.)and must also include plans and cross section or profile drawings
showing the location, character,and dimensions of all proposed activities and aquatic resource impacts.
The owner wants to know where the approved edge is located before starting the planning process.As soon as approval is
received they will move forward with their project.
PART FOUR: Aquatic Resource Impactl Summary
If your proposed project involves a direct or indirect impact to an aquatic resource (wetland, lake, tributary, etc.) identify each
impact in the table below. Include all anticipated impacts, including those expected to be temporary. Attach an overhead view
map, aerial photo, and/or drawing showing all of the aquatic resources in the project area and the location(s) of the proposed
impacts. Label each aquatic resource on the map with a reference number or letter and identify the impacts in the following table.
Aquatic Type of Impad Duration of Existing Plant County,Major
Aquatic Resource Overall Size of Watershed#,
Resource Type (fill,excavate, Impact Z Community
ID(as noted on Size of Impact Aquatic and Bank Service
(wetland,lake, drain,or remove Permanent(P)or 3 Type(s)in Impact
overhead view) 1 Resource , Area#of Impact
tributary etc.) vegetation) Temporary(T) Area
Areas
'If impacts are temporary;enter the duration of the impacts in days next to the"T". For example,a project with a temporary access fill that would be removed
after 220 days would be entered"T(220)".
Zlmpacts less than 0.01 acre should be reported in square feet. Impacts 0.01 acre or greater should be reported as acres and rounded to the nearest 0.01 acre.
Tributary impacts must be reported in linear feet of impact and an area of impact by indicating first the linear feet of impact along the flowline of the stream
followed by the area impact in parentheses). For example,a project that impacts 50 feet of a stream that is 6 feet wide would be reported as 50 ft(300 sq/ft).
3This is generally only applicable if you are applying for a de minimis exemption under MN Rules 8420.0420 Subp.8,otherwise enter"N/A".
°Use Wetlond Plants and Plont Community Types of Minnesota ond Wisconsin 3rd Ed.as modified in MN Rules 8420.0405 Subp.2.
SRefer to Major Watershed and Bank Service Area maps in MN Rules 8420.0522 Subp.7.
If any of the above identified impacts have already occurred,identify which impacts they are and the circumstances associated
with each:
PART FIVE: Applicant Signature
❑ Check here if you are requesting a pre-application consultation with the Corps and LGU based on the information you have
provided. Regulatory entities will not initiate a formal application review if this box is checked.
By signature below, I attest that the information in this application is complete and accurate. I further attest that I possess the
authority to undertake the work described herein.
Signature: `�`^ � d Date: October 22, 2014
I hereby authorize Svoboda Ecological Resources to act on my behalf as my agent in the processing of this application and to
furnish, upon request,supplemental information in support of this application.
1 The term"impact"as used in this joint application form is a generic term used for disclosure purposes to identify
activities that may require approval from one or more regulatory agencies. For purposes of this form it is not meant to
indicate whether or not those activities may require mitigation/replacement.
Project Name and/or Number: SER#2014-031-03—225 Old Crystal Bay Road N,Orono
Attachment A
Request for Delineation Review, Wetland Type Determination, or
�urisdictional Determination
By submission of the enclosed wetland delineation report, I am requesting that the U.S.Army Corps of Engineers,St. Paul District
(Corps)and/or the Wetland Conservation Act Local Government Unit(LGU) provide me with the following(check all that apply):
�Wetland Type Confirmation
�Delineation Concurrence. Concurrence with a delineation is a written notification from the Corps and a decision from the LGU
concurring, not concurring,or commenting on the boundaries of the aquatic resources delineated on the property. Delineation
concurrences are generally valid for five years unless site conditions change. Under this request alone,the Corps will not address
the jurisdictional status of the aquatic resources on the property, only the boundaries of the resources within the review area
(including wetlands,tributaries, lakes,etc.).
❑ Preliminary lurisdictional Determination.A preliminary jurisdictional determination (PJD)is a non-binding written indication
from the Corps that waters,including wetlands, identified on a parcel may be waters of the United States. For purposes of
computation of impacts and compensatory mitigation requirements, a permit decision made on the basis of a PJD will treat all
waters and wetlands in the review area as if they are jurisdictional waters of the U.S. PJDs are advisory in nature and may not be
appealed.
❑Approved Jurisdictional Determination.An approved jurisdictional determination (AJD)is an official Corps determination that
jurisdictional waters of the United States are either present or absent on the property.AJDs can generally be relied upon by the
affected party for five years.An AJD may be appealed through the Corps administrative appeal process.
In order for the Corps and LGU to process your request,the wetland delineation must be prepared in accordance with the 1987
Corps of Engineers Wetland Delineation Manual,any approved Regional Supplements to the 1987 Manual,and the Guidelines for
Submitting Wet/and Delineations in Minnesota(2013).
http://www.mvp.usace.armv.mil/Missions/Re�ulatorv/DelineationJDGuidance.asqx
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