HomeMy WebLinkAboutWetland Classification/Identification/Delineation-2013 Christine Mattson
From: Wes D. Boll [wboll@wenck.com]
Sent: Thursday, December 26, 2013 8:45 AM
To: 'Erica Britcher'; 'Brandon Wisner'; Christine Mattson; 'Peterson, Lynda (BWSR)'; 'Stacey
Lijewski'; Melissa.m.jenny@usace.army.mil
Cc: 'Frank Svoboda'; boberta50@msn.com
Subject: RE: 835 Hunt Farm Rd, Orono
Since this wetland delineation report was received outside of the growing season,the MCWD will consider it to be
incomplete until field conditions allow us to review the boundary. The Notice of Application for this wetland delineation
will be issued in Spring 2014.
Let me know if you have any questions.
Wes
Wes Boll, Environmental Scientist
Wenck Associates Inc., 1800 Pioneer Creek Ctr., P.O. Box 249, Maple Plain, MN 55359-9000
www.wenck.com �, wbollCa�wenck.com � D 763.479.4283 � F 763.479.4242 � G 763.479.4200 � C612.518.6592 �
From: Erica Britcher [mailto:ericabCa>gpsinnovations.com]
Sent: Thursday, December 19, 2013 3:02 PM
To: 'Brandon Wisner'; 'Christine Mattson'; 'Peterson, Lynda (BWSR)'; 'Stacey Lijewski'; Melissa.m.jennvCa�usace.army.mil;
Wes D. Boll
Cc: 'Frank Svoboda'; boberta50@msn.com
Subject: 835 Hunt Farm Rd, Orono
Attached is our wetland delineation report for the above mentioned property. Please let us know
if you would like a paper copy. Any questions should be addressed to Frank Svoboda. We
understand that this will not be able to be reviewed in the field until Spring and get final
approval since the growing season has passed for this year. Thank you for working with us on
this project.
Erica Britcher
Professional Services Manager
Svoboda Ecological Resources
25580 Nelsine Drive
Shorewood, MN 55331
952-471-1100
i
Christine Mattson
From: Erica Britcher[ericab@gpsinnovations.com]
Sent: Thursday, December 19, 2013 3:02 PM
To: 'Brandon Wisner'; Christine Mattson; 'Peterson, Lynda (BWSR)'; 'Stacey Lijewski';
Melissa.m.jenny@usace.army.mil; 'Wes D. Boll'
Cc: 'Frank Svoboda'; boberta50@msn.com
Subject: 835 Hunt Farm Rd, Orono
Attachments: 2013-040 835 Hunt Farm Rd Wetland Delin Report.pdf; DOC121913.pdf
Attached is our wetland delineation report for the above mentioned property. Please let us know
if you would like a paper copy. Any questions should be addressed to Frank Svoboda. We
understand that this will not be able to be reviewed in the field until Spring and get final
approval since the growing season has passed for this year. Thank you for working with us on
this project.
Erica Britcher
Professional Services Manager
Svoboda Ecological Resources
25580 Nelsine Drive
Shorewood, MN 55331
952-471-1100
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Prouiding t.he Sharper Edge in
Natural Resources &Ennironrraental Cohsulting
ECOL�GICAL RESOURCES
:� - � �� , - ��
' 11 ' 111
83 5 Hunt Farm Rd
Orono, Hennepin County, l�'IN
Wetland Classification, Identification, and
Delineation Report
Prepared for:
Bob Angen,Masonry Builders
By:
Svoboda Ecological Resources
Project Number 2013-040
11/26/2013
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..............................................................................................................................................3
REC OMMENDATIONS............................................................................................................................3
CERTIFICATION......................................................................................................................................5
DATASOURCES........................................................................................................................................6
LITERATUREREFERENCED................................................................................................................7
FIGURES:
Figure 1: Site Location Overlaid on Topographic Map
Figure 2: National Wetlands Inventory
Figure 3: Web Soil Survey-Hennepin County
Figure 4: Public Waters Inventory
Figure 5: Approximate Wetland Boundary and Sample Point Location
TECHNICAL DOCUMENTS:
Photo Log
Field Data Sheets
Plant Indicator Status
Soil Series Data
ABSTRACT
Svoboda Ecological Resources (SER) visited the above referenced property on 11/23/13 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. One sample transect was established along the western boundary of the eastern
wetland area and one along the eastern side of the western wetland in order to characterize the
soil, vegetation, and existing hydrology within the wetland-to-upland transition zone.
INTRODUCTION
The subject parcel at 835 Hunt Farm Rd is approximately 3.37 acres. The parcel is an upland
woodlands, with a few open grassy areas and a ditch running between the two wetlands on the
east and west sides. The ditch becomes an excavated (but currently dry) pond on the east side of
the property. The topography of the site is rolling and elevated between the two wetlands.
Numerous huge boulders are present on the lot along with many patches of reed canary grass.
The surrounding land use is primarily widely spaced single family homes and wetlands. The
identified wetlands were 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 subject 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
Svoboda Ecological Resources 1 835 Hunt Farm Rd
Project Number: 2013-040 Orono MN
wetland boundaries." "...This Regional Supplement is designed for use with the
current version of the Corps Manual (Environmental Laboratory 1987) and all
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 2), 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 List of Plant Species That Occur in Wetlands —
Region 3 (Sabine 1999).
RESULTS
The National Wetland Inventory indicates the presence of two wetlands in the survey area. The
western wetland is categorized as PF06Cd while the eastern wetland is labeled PEMC (Figure
2).
The Web Soil Survey of Hennepin County (Figure 3) identifies three soil map units present on
the subject property. They are as follows: Klossner soils, depressional; Hamel-Glencoe,
depressional, complex; and Angus-Kilkenny complex. The Klossner type is the hydric soil on the
site. The Hamel-Glencoe type is predominantly hydric while the Angus-Kilkenny is
predominantly nonhydric. Soil series descriptions are provided in the Technical Documents
section.
The Minnesota Department of Natural Resources, State Protected Waters Map (Public Water
Inventory) indicates no public water wetland 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(Figure 5).
Svoboda Ecological Resources 2 835 Hunt Fann Rd
Project Number: 2013-040 Orono,MN
The NWI identified the western wetland as PF06Cd. The wetland is mainly an emergent
herbaceous marsh that does have some wooded areas along the edges and to the south. T'he
wetland would likely better be categorized as PEM/F06Cd. Vegetation in the seasonally
inundated wetland was dominated by cattail (likely both Typha latifolia OBL and Typha X glauca
OBL) and reed canarygrass (Phalaris arundinacea FACW) around the edges as well as red osier
dogwood (Cornus sericea FACW) around some edges. Transition to uplands is marked by slope
or beginning of more robust woodlands.
Transect SP 1-1 was taken from the east side of the western wetland roughly where the ditch
connects to the wetland. The soils at sample point SP 1-1 Wet consisted of a mucky loam at the
surface with loamy clay and other clay layers beneath. Hydric indicators A10 (2 cm Muck) and
Al2 (Thick Dark Surface) were present. The soils at sample point SP 1-1 Up consisted of layers
of loam at the surface with silty layers below. Hydric indicator F6 (Redox Dark Surface) was
present.
At sample point SP 1-1 Wet hydrology indicator C7 (Thin Muck Surface) and secondary
indicator D2 (Geomorphic Position) were present. Wetland hydrology was not indicated at
sample point SP 1-1 Up.
Wetland 2 is identified by the NWI as PEMC. The seasonally inundated wetland is an emergent
herbaceous depression. The transition to upland can be marked as the canarygrass gives way to
woodland.
The transect SP 2-1 was taken from the northeast side of the western portion of the seasonally
inundated wetland. The soils at sample point SP 2-1 Wet consisted of a muck loam at the surface
with loams and clays beneath. Hydric indicators A10 (2 cm Muck) and Al2 (Thick Dark
Surface)were present. Surface water was present at this point and the water table was at 2 inches
and saturation at 0 inches. The soils at sample point SP 2-1 Up consisted of several loamy layers.
Hydric indicatorAl2 (Thick Dark Surface)was present.
At sample point SP 2-1 Wet hydrology indicator C7 (Thin Muck Surface) and secondary
indicators D2 (Geomorphic Position) and DS (FAC-Neutral) were present. Wetland hydrology
was not indicated at sample point SP 2-1 Up.
A constructed ditch connecting the two wetlands through obvious upland was also flagged and
designated as a ditch.
The site contains many huge boulders of unknown origin as well as numerous patches of reed
canary grass scattered throughout the upland area. It appears that a mobile home site may have
been present just off the parcel to the southwest. A formerly metered power outlet pedestal was
observed at that location.
The presence of scattered reed canary grass throughout the site suggests the possible disposal of
silty soil across the property at some time in the past,perhaps as topsoil augmentation.
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 3 835 Hunt Fazm Rd
Project Number: 2013-040 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. Hydric soils were indicated on both upland
sample points and the predominance of reed canarygrass on open hilly areas on the parcel is
therefore not surprising. The site visit portion of the wetland delineation was completed on
11/23/13.
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.
1* State jurisdiction by the Wetland Conservation Act of 1991 (WCA) administered by the
WCA Local Governmental Unit(LGU).
2* 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 only three 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 4 835 Hunt Fann Rd
Project Number: 2013-040 Orono,MN
CERTIFICATION
David Remucal and Frank Svoboda completed the above-described delineation on 11/23/2013.
This delineation was performed according to the procedures described by the US Army Corps of
Engineers in the 1987 Wetlands Delineation Manual and the 2007 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 force at the time the
delineation was completed.
Report and graphics were prepared by David Remucal (Wetland Ecologist)on this day
11/26/2013.The delineation report was reviewed by Frank Svoboda,President of Svoboda
Ecological Resources.
Client: Bob Angen, Masonry Builders
Project Name:835 Hunt Farm Rd
Project No.: 2013-040
Location: Orono, MN
��X�eh `��a.e�,i/��.f�.
GIS Technician
� "
Wetland Ecologist
c�Je-eu+��--- d'
President, Svoboda Ecological Resources
12/3/13
Date
Svoboda Ecological Resources $ 835 Hunt Farm Rd
Project Number: 2013-040 Orono IVIN
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/Data/Mapper.html on 5/28/12.
2010 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.nres.usda.gov/app/HomePage.htm
Svoboda Ecological Resources 6 835 Hunt Fazm Rd
Project Number: 2013-040 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. 2011. 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. 91 Opp.
Lichvar, R.W. 2013. The National Wetland Plant List: 2013 wetland ratings. Phytoneuron
2013-49: 1-241. http://rs�isias.crrel.usace.army.mil/NWPL/
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 � 835 Hunt Farm Rd
Project Number. 2013-040 Orono MN
FIGURES
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T11�N `��'`� �'0 A roximate Wetland Bounda�-v �'igure s
T118N R23W S31 pp ` J
Overlaid on 2012 Aerial Photo
!���.SVOBODA 2013-040
0 100 200 400 835 Hunt Farm Rd
l; � Ecologica! Resources Feet Orono, MN
THE TECHNICAL DOCUMENTATION SECTION
Field Data Sheets
WETLAND DETERMINATION DATA FORM-Midwest Region
ProjecUSite 835 Hunt Fartn Rd City/County: Orono/Hennepin Sampling Date: 11/23/2013
ApplicanUOwner: BobAngen State: MN Sampling Point: SP 1-1 Up
Investigator(s): DR,FJS >ection,Township,Range: T118N R23W S30/S31
Landform(hillslope,terrace,etc.): hillslope Local relief(concave,convex,none): convex
Slope(%): 5.00% Lat: Long: Datum: NAD83
Soil Map Unit Name Hamel-Glencoe,depressional,complex,0 to 3 percent slopes JWI Class�cation: None
Are GimatiGhydrologic conditions of the site typical for this time of the year? Y (If no,explain in remarks)
Are vegetation ,soil ,or hydrology sign'rficantly disturbed? Are"nortnal circumstances"
Are vegetation ,soil ,or hydrology naturally problematic? present? Yes
SUMMARY OF FINDINGS (If needed,explain any answers in remarks.)
Hydrophytic vegetation presenY? Y
Hydric soil present? Y Is the sampled area within a wetland? N
Indicators of wetland hydrology present? N `yes,optional wetland site ID:
Remarks:(Explain altemative procedures here or in a separete report.)
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 Quercus rubre 25 Y FACU that are OBL,FACw,or FAC: 2 (A)
2 Total Number of Dominant
3 Speaes Across all Strata: 4 (B)
4 Percent of Dominant Species
5 that a2 OBL,FACW,or FAC: 50.00% (A/B)
25 =Total Cover
Sa�lina/Shrub straturt (Plot size: 15' ) Prevalence Index Worksheet
1 Rhamnus cathartica 25 Y FAC Total°k Cover of:
z OBL species 0 x 1= 0
3 FACW species 80 x 2= 160
4 FAC species 25 x 3= 75
5 FACU species 45 x 4= 180
25 =Total Cover UPL species 0 x 5= 0
Herb stratum (Plot size: 5' ) Column totals 150 (A) 415 (B)
1 Phalaris arundinacea 80 Y FACW Prevalence Index=B/A= 2.77
2 Solidago canadensis 20 Y FACU
3 Hydrophytic Vegetation Indicatois:
4 Rapid test for hydrophytic vegetation
5 Dominance test is>50°h
6 X Prevalence index is 53.0'
7 Morphogical adaptations*(provide
8 supporting data in Remarks or on a
g separate sheet)
10 Problematic hydrophytic vegetation'
100 =Total Cover (explain)
Woodv vine stratum (PIOt Size: 30� ) 'Indicatws of hydric sdl antl wetlantl hydrology must be
� present,unless disturbed or problematic
2 rop
0 =Total Cover Ve9�O°
preseM7 Y
Remarks:(Indude photo numbers here or on a separate sheet)
US Amy Corps of Engineers Midwest Region
SOIL Sampling Point: SP 1-1 Up
Proftle Description: (Descrlbe to the depth needed to document the indicator or conflrtn the absence of fndicators.)
Depth Matrix Redox Features
(Inches) Color(moist) % Color(moist) % Type' Loc*' Texture Remarks
4 10YR 2/1 100 Loam
14 10YR 2/1 95 10YR 7/6 5 C PUM Silt loam
21 10YR 2/1 100 Silt Gay
'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(SS) 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 Surtace(TF12)
2 cm Muck(A10) Depleted Matrix(F3) Other(explain in remarks)
Depleted Below Oark Surface(A11) X Redox Dark Surface(F6)
Thick Dark Surface(Al2) Depleted Dark Surface(F7) 'Indicators of hydrophytic vegetation and weltand
Sandy Mucky Minerel(S1) Redox Depressions(F8) hydrology must be present,unless disturbed or
problematic
RestricUve Layer(if observed):
Type: Hydrlc soil present? Y
Depth(inches):
ema s:
HYDROLOGY
WeUand Hydrology Indicators:
Primarv Indicators(minimum of one is reauired:check all that ao�lv) Sec I dicators minimum of two re uired
Surtace Water(A1) Aquatic Fauna(613) Surtace Soil Credcs(B6)
High Water Table(A2) True Aquatic Plants(614) Drainage Pattems(610)
Sffiuratio�(A3) Hydrogen Su�de Odor(C1) Dry-Season WaterTable(C2)
Water Marks(61) Oxidized Rhizospheres on Living Roots Crayflsh Burrows(C8)
Sediment Deposits(62) (C3) Saturation vsible on Aerial Imagery(C9)
Drift Deposits(B3) Presence W Reduced Iron(C4) Stunted or Stressed Plants(D1)
Algal Mat or Crust(B4) Recent Iron Reduction in Tilled Soils Geomorphic Position(D2)
Iron Deposits(B5) (C6) FAC-Neutrel Test(D5)
Inundation Vsible on Aerial Imagery(67) Thin Mudc Surface(C7)
Sparsely Vegetated Concave Surface(BS) Gauge or Well Data(D9)
Water-Stained Leaves(89) Other(Explain in Remarks)
e erva ons:
Surface water presenY? Yes No X Depth(inches):
Watertable present? Yes No �—Depth(inches): Indicators ofwetland
Saturation present? Yes No �Depth(inches): hydrology present7 N
(inGudes capillary fringe)
Describe recorded data(stream gauge,monitoring well,aerial photos,previous inspections),if available:
ema s:
US Army Corps of Engineers Midwest Region
WETLAND DETERMINATION DATA FORM-Midwest Region
ProjecUSke 835 Hunt Fartn Rd City/County: Orono/Hennepin Sampling Date: 11/23/2013
ApplicanUOwner: Bob Angen State: MN Sampling Point: SP 1-1 Wet
Investigator(s): DR,FJS >ection,Township,Range: T118N R23W S30/S31
Landform(hilislope,terrace,etc.): hillslope Local relief(concave,convex,none): convex
Slope(%): 5.00°k Lat: Long: Datum: NAD83
Soil Map Unit Name Hamel-Glencoe,depressional,complex,0 to 3 percent slopes JWI Class�cation: PF06Cd
Are Gimatic/hydrologic conditions of the site typical for this time of the year? Y (If no,explain in remarks)
Are vegetation ,soil ,or hydrology significantly disturbed? Are"nortnal 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 wetland? Y
Indicators of wetland hydrology present? Y `yes,optional weUand site ID:
Remarks:(Explain altemative procedures here or in a separate report.)
NWI and parcel boundaries don't appear accurate in maps,they appear to overlap on the ground.NWI polygon does ot
line up with wetland on the imagery.
VEGETATION--Use scientific names of plants.
Absolute Dominan Indicator pominance Test Worksheet
Tree Stratum (Plot size: 30' ) °h Cover t Species Staus Number of Dominant Species
1 Quercus rubra 10 Y FACU that are OBL,FACW,or FAC: 4 (A)
2 Quercus macrocarpa 10 Y FAC Tatal Number of Dominant
3 Acer negundo 10 Y FAC Specias Across all Svata: 5 (B)
4 Percent of Dominant Species
5 that are OBL,FACW,or FAC: 80.00% (AIB)
30 =Total Cover
Saolina/Shrub sUaturt (Plot size: 15' ) Prevalence Index Worksheet
1 Rhamnus cathartica 30 Y FAC Total°k Cover of:
Z OBL species 0 x 1= 0
3 FACW species 100 x 2= 200
q FAC species 50 x 3= 150
5 FACU species 10 x 4= 40
30 =Total Cover UPL species 0 x 5= 0
Herb sVatum (Plot size: 5' ) Column totals 160 (A) 390 (B)
1 Phalans arundinacea 100 Y FACW Prevalence Index=B/A= 2.44
2
3 Hydrophytic Vegetation Indicators:
q Rapid test for hydrophytic vegetation
5 X Dominance test is>50%
g X Prevalence index is 53.0*
7 Morphogical adaptations'(provide
8 supporting data in Remarks or on a
g separate sheet)
10 Problematic hydrophytic vegetation"
100 =Total Cover (explain)
Woodv vine stratum (Plot size: 30' ) •Indicators a nydric sai and wenand hydrolapy must ne
� present,unless disturbed or problematic
2 y rop c
0 =Total Cover �e9�tion
present? Y
Remarks:(Indude photo numbers here or on a separate sheet)
US Amy Corps of Engineers Midwest Region
SOIL Sampling PoiM: SP 1-1 Wet
Proflle Deacription: (Describe to the depUi needed to document the Indicator or conflrm the absence of indicators.)
Depth Matrix Redox Features
(Inches) Color(moist) °h Color(moist) % Type' Loc** Texture Remarks
3 10YR 2/1 100 Muck loam
12 10YR 2/1 100 Loamy Gay
15 10YR 2/1 70 SGY 6/1 30 D M Silt clay
20 5GY 6/1 70 10YR 5/4 5 C PL Clay
20 10YR 2/1 25
'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)
Bladc 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(AS) Loamy Gleyed Matrix(F2) Very Shallow Dark Surface(TF12)
X 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 Surtace(F7) 'Indicators of hydrophytic vegetation and weltand
Sandy Mucky Mineral(S1) Redox Depressions(FS) hydrology must be present,unless disturbed or
— — problematic
Restrictive Laye►(if observed):
Type: Hydric soil present? Y
Depth(inches):
ema s:
HYDROLOGY
Wetland Hydrology Indicators:
Primarv Indicators(minimum of one is reauired:check all that anolvl econda Indicator i 'm m of two re ui d
Surtace Water(A1) Aquabc Fauna(B13) Surtace Soil Cracks(B6)
High Water Table(A2) True Aquatic Plants(614) Drainage Pattems(B10)
Saturation(A3) Flydrogen Su�de Odor(C1) Dry-Season Water Table(C2)
Water Marks(B1) O�adized Rhizospheres on Living Roots Crayfish Burrowa(C8)
Sediment Deposits(62) (C3) Saturation Visible on AeAal Imagery(C9)
Drift Deposits(B3) Prese�ce of Reduced Iron(C4) Stunted or Stressed Plants(D1)
Algal Mat or Crust(B4) Recent Iron Reducfion in Tilled Soils �Geomoiphic Position(D2)
Iron Deposila(B5) (C6) _FAC-Neutral Test(D5)
Inundation Vsible on Aerial Imagery(B7) X Thin Mudc Surtace(C�
Sparsely Vegetated Concave Surtace(BS) Gauge or Well Data(D9)
Water-Stained Leaves(68) Other(E�lain in Remarks)
e erv ons:
Surtace water present? Yes No X Depth(inches):
Water table present? Yes No T Depth(inches): Indicators of wetland
Saturation present? Yes No —S�Depth(inches): hydrology present? Y
(includes capillary fringe)
Describe recorded data(stream gauge,monitoring well,aerial photos,previous inspections),if available:
emarks:
Ground is beginning to freeze so saturation and water tabie may not be readable
US Army Corps of Engineers Midwest Region
WETLAND DETERMINATION DATA FORM-Midwest Region
ProjecVSite 835 Hunt Farm Rd City/County: Orono/Hennepin Sampling Date: 11/23/2013
ApplicanUOwner: Bob Angen State: MN Sampling Point: SP 2-1 Up
Investigator(s): DR,FJS iection,Township,Range: T118N R23W S30/S31
Landform(hillslope,terrace,etc.): hillslope Local relief(concave,convex,none): none
Slope(%): 3.00°k Lat: Long: Datum: NAD83
Soil Map Unit Name Klossner soils,depressional,0 to 1 percent slopes JWI Class�cation: none
Are dimatiGhydrologic conditions of the site typical for this time of the yea�'? Y (If no,explain in remarks)
Are vegetation ,soil ,or hydrology sign�cantly disturbed? Are"nortnal 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 wetland? N
Indicators of weUand hydrology present? N `yes,optional wetland site ID:
Remarks:(Explain alternative procedures here or in a separate report.)
VEGETATION—Use saentific names of plants.
Absolute Dominan Indicator pominance Test Worksheet
Tree Stratum (Plot size: 30' ) %Cover t Species Staus Number of Dominant Species
1 Acersaccharum 80 Y FACU that are OBL,FACW,or FAC: 3 (A)
2 Total Number of Dominant
3 Species Across all Strata: 5 (B)
4 Percent of Dominant Species
5 that are OBL,FACW,or FAC: 60.00% (A/B)
80 =Total Cover
Sa�lina/Shrub stratun (Plot size: 15' ) Prevalence Index Worksheet
1 Ulmus americana 10 Y FACW Total°k Cover of:
2 Rhamnus cathartica 10 Y FAC OBL species 0 x 1= 0
3 FACW species 15 x 2= 30
q FAC species 10 x 3= 30
5 FACU species 85 x 4= 340
20 =Total Cover UPL species 0 x 5= 0
Herb stratum (Plot size: 5' ) Column totala 110 (A) 400 (B)
1 Phalaris arundinacea 5 Y FACW Prevalence Index=B/A= 3.64
2 Glechoma hederacea 5 Y FACU
3 Solidago sp. 2 N Hydrophytic Vegetation Indfcators:
4 Rapid test for hydrophytic vegetation
5 X Dominance test is>50°�
g Prevalence index is 53.0'
7 Morphogical adaptations"(provide
8 suppoRing data in Remarks or on a
g separete sheet)
10 Problematic hydrophytic vegetation*
12 =Total Cover (e�lain)
WoodV Vi�B Stfatum (PIOt SiZB: 30' ) 'Indicators of hydric soil and wetland hydrology must be
� present,unless disturbed or problematic
2 y rop c
0 =Total Cover �e9etation
present? Y
Remarks:(InGude photo numbers here or on a separate sheet)
US Amy Corps of Engineers Midwest Region
SOIL Sampling Point: SP 2-1 Up
Proflle Desc�iption: (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
3 10YR 2/1 100 Loam Organic matter
24 10YR 2/1 100 Loam
30 10YR 2/1 20 10YR 6/2 SO D M Clay loam
'Type:C=Concentration,D=Depletion,RM=Reduced Matrix,MS=Masked Sand Grains. '*Location:PL=Pore Lining,M=Matrix
Hydric Soil Indicators: Indicators for Problematic Hyd�ic Solls:
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 Minerel(F1) Iron-Manganese Masses(F12)(LRR K,L,R)
Stratified Layers(AS) Loamy Gleyed MaVix(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 Surtace(F7) 'Indicators of hydrophytic vegetation and weltand
Sandy Mucky Mineral(S1) Redox Depressions(F8) hydrology must be p2sent,unless disturbed or
— — problematic
Restricfive Layer(if observed):
Type: Hydric soil present? Y
Depth(inches):
ema s:
HYDROLOGY
Wetland Hydrology Indicators:
Primarv Indicators(minimum of one is reauired:check all that aoelv) Secondarv Indicators(minimum of two reauired)
Surface Water(A1) Aquatfc fauna(813) Surtace Soil Crecks(BB)
High Water Table(A2) True Aquatic Plants(B74) Dreinage Patlems(B10)
Saturation(A3) Hydrogen Sulfide Odor(C1) Dry-S�son Weter Table(C2)
Water Marks(81) Oxidized Rhizospheres on living Roots Crayfish Burtows(C8)
Sediment Deposits(82) (C3) Saturation vsible on Aerial Imagery(C9)
Drift Deposits(63) 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 Vsible on Aerial Imagery(B7) Thin Muck Surtace(C7)
Sparsey Vegetated Concave Surface(68) Gauge or Well Data(D9)
Water-Stained Leaves(B9) Other(Explain in Remarks)
�e ervabons:
Surface water presenY? Yes No X Depth(inches):
Water table presenY? Yes No �Depth(inches): Indicators of wetland
Saturation present? Yes No X Depth(inches): hydrology present? N
(inGudes capillary fringe)
Describe recorded data(stream gauge,monitoring well,aerial photos,previous inspections),'rf available:
emarks:
US Army Corps of Engineers Midwest Region
WETLAND DETERMINATION DATA FORM-Midwest Region
ProjecUSite 835 Hunt Fartn Rd City/County: Orono/Hennepin Sampling Date: 11/23/2013
ApplicanUOwner: Bob Angen State: MN Sampling Point: SP 2-1 Wet
Investigator(s): DR,FJS >ection,Township,Range: T118N R23W S30/S31
Landform(hillslope,terrace,etc.): depression Local relief(concave,convex,none): none
Slope(%): 0.00°h Lat: Long: Datum: NAD83
Soil Map Unit Name Klossner soils,depressional,0 to 1 percent slopes JWI Classification: PEMC?
Are GimatiGhydrologic conditions of the site typical for this time of the year? Y (If no,explain in remarks)
Are vegetation ,soil ,or hydrology sign�cantly disturbedT Are"normal circumstances"
Are vegetation ,soil ,or hydrology naturally problematic? present?
SUMMARY OF FINDINGS (If needed,explain any answers in remarks.)
Hydrophytic vegetation presenY? Y
Hydric soil present? Y Is the sampled area wkhin a wetland? Y
Indicators of weUand hydrology present? Y `yes,optional weUand site ID:
Remarks:(Explain alternative procedures here or in a separete report.)
NWI and parcel boundaries don't appear accurate in maps,they appear to overlap on the ground.NWI polygon does ot
match wetland edge on aerial photo.
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 Acersaccharum 20 Y FACU that are OBL,FACW,or FAC: 4 (A)
2 Quercus macrocarpa 5 Y FAC Total Number of Dominant
3 Species Across all Streta: 5 (B)
4 Percent of Dominant Species
5 that are OBL,FACW,or FAC: 80.00% (A/B)
25 =Total Cover
Sa�lina/Shrub stratun (Plot size: 15' ) Prevalence Index Worksheet
1 Comus racemosa 30 Y FAC Total�o Cover of:
2 Acersaccharum 5 N FACU OBL species 40 x 1= 40
3 FACW species 60 x 2= 120
4 FAC species 35 x 3= 105
g FACU species 25 x 4= 100
35 =Total Cover UPL species 0 x 5= 0
Herb stratum (Plot size: 5' ) Column totals 160 (A) 365 (B)
1 Phalaris arundinacea 50 Y FACW Prevalence Index=B/A= 2.28
2 Carex sbicfa 30 Y OBL
3 Onoclea sensibilis 10 N FACW Hydrophytic Vegetation Indicators:
4 Typha IatiPolia 10 N OBL Rapid test for hydrophytic vegetation
5 X Dominance test is>50°h
g X Prevalence index is 53.0'
7 Morphogical adaptations'(provide
g supporting data in Remarka or on a
g separete sheet)
10 Problematic hydrophytic vegetation*
100 =Total Cover (explain)
WoodY vine sVetum (Plot SIZe: 30' ) •Indicetors of hydric sal and wetland hydrolagy must be
� present,unless distuibed or problematic
2 y rop ic
0 =Total Cover vegetation
present? Y
Remarks:(Indude photo numbers here or on a separate sheet)
US Amy Corps of Engineers Midwest Region
SOIL SampHng Point: SP 2-1 Wet
Proflle Description: (Deacribe to the depth needed to document the indicator or conBrtn the absence of indfcators.)
Depth Matrix Redox Features
(Inches) Color(moist) °k Color(moist) % Type* Loc" Texture Remarks
4 10YR 3/1 100 Muck loam
10 10YR 3/1 100 Loam
16 10YR 3/1 100 Silt loam
18 10YR 2/1 90 10YR 6/1 10 D PUM Clay loam
24 2.5Y 8/2 60 10YR 6/1 40 D M 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 Matriu(S4) Coast Prairie Redox(A16)(LRR K,L,R)
Histic Epipedon(A2) Sandy Redox(S5) Dark Surtace(S7)(LRR K,L)
Black Histic(A3) SVipped 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)
Strat�ed Layers(AS) Loamy Gleyed Matrix(F2) Very Shallow Dark Surface(TF12)
X 2 cm Muck(A10) Depleted Matrix(F3) Other(explain in remarks)
Depleted Below Dark Surface(A11) Redox Dark Surface(F6)
X Thick Dark Surtace(Al2) Depleted Dark Surtace(F7) *Indicators of hydrophy6c vegetation and weltand
Sandy Mucky Mineral(S1) Redox Depressions(F8) hydrology must be present,unless disturbed or
— problematic
Restrtctive Layer(if observed):
Type: Hydric soil present4 Y
Depth(inches):
emarks:
HYDROLOGY
WeUand Hydrology Indicators:
Primarv Indicators(minimum of one is reauired:check all that ao�lv) Secondarv Indicators(minimum of two re ire
Surface Water(A1) AquaUc Fauna(613) Surtace Soil Crecks(BB)
High Water Table(AZ) True Aquatic Plants(614) Drainage Pattems(610)
Sffiuration(A3) Hydragen Sulfide Odor(C1) Dry-Season Water Table(C2)
Water Marks(61) Oxidized Rhizospheres on Living Roots Crayfish Burrows(C8)
Sediment Deposits(82) (C3) Saturation vsible on Aerial Imagery(C8)
DriR Deposits(B3) Presence of Reduced Iron(C4) Stunted or Stressed Plants(D1)
Algal Mat or Crust(64) Recent Iron Reductlon in Tilled Soils �Geomorphic Position(D2)
Iron Deposits(65) (C6) �FAC-Neutral Test(D5)
Inundation Vsible on Aerial Imagery(B7) X Thin Muck Surtace(C7)
Sparsely Vegetated Concave Surtace(B8) Gauge or Well Data(D9)
Water-Stained Leaves(B9) Other(Explain in Remarks)
�e erva ons:
Surtace water presenY? Yes No X Depth(inches):
Water table present? Yes No X Depth(inches): Indicators of weUand
Saturation presenY? Yes No X Depth(inches): hydrology present? Y
(inGudes capillary fringe)
Describe recorded data(stream gauge,monitoring well,aerial photos,previous inspections),if available:
emarks:
Ground is beginning to freeze so saturation and water table may not be readable
US Army Corps of Engineers Midwest Region
WETLAND DETERMINATION DATA FORM-Midwest Region
Project/SRe 835 Hunt Fartn Rd City/County: Orono/Hennepin Sampling Date: 11/23/2013
ApplicanUOwner: Bob Angen State: MN Sampling Point: SP 2-1a Up
Investigator(s): DR,FJS iection,Township,Range: T118N R23W S30/S31
Landform(hillslope,terrace,etc.): hillslope Local relief(concave,convex,none): none
Slope(°k): 3.00�o Lat: Long: Datum: NAD83
Soil Map Unit Name Klossner soils,depressional,0 to 1 percent slopes �WI Class�cation: none
Are Gimatic/hydrologic conditions of the site typical for this time of the yeaR Y (If no,e�lain in remarks)
Are vegetation ,soil ,or hydrology sign'rficantly disturbed? qre"nortnal circumstances"
Are vegetation ,soil ,or hydrology naturally problematic? present7 Yes
SUMMARY OF FINDINGS (If needed,explain any answers i�remarks.)
Hydrophytic vegetation present? N
Hydric soil present? Y Is the sampled area within a wetland? N
Indicators of wetland hydrology present? N 'yes,optional wetland site ID:
Remarks:(E�lain alternative procedures here or in a separate report.)
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 Acersaccharum 80 Y FACU that are OBL,FACW,or FAC: 2 (A)
2 Total Number of Dominant
3 Species Across all Strata: 4 (B)
4 Percent of Dominant Species
5 that are OBL,FACW,or FAC: 50.00% (A/B)
80 =Total Cover
Saolina/Shrub straturt (Plot size: 15' ) Prevalence Index Worksheet
1 Ulmus americana 10 Y FACW Total°�Cover of:
2 Rhamnus cethartica 10 Y FAC OBL species 0 x 1= 0
3 FACW species 15 x 2= 30
4 FAC species 10 x 3= 30
5 FACU species 85 x 4= 340
20 =Total Cover UPL species 15 x 5= 75
Herb sVatum (Plot size: 5' ) Column totals 125 (A) 475 (B)
1 Carex pensyNanica 15 Y UPL Prevalence Index=B/A= 3.80
2 Glechoma hederacea 5 N FACU
3 Phalaris arundinacea 5 N FACW Hydrophy8c Vegetation lodicators:
4 Solidago sp. 2 N Rapid test for hydrophytic vegetation
5 Dominance test is>50%
g Prevalence index is 53.0*
7 Morphogical adaptations*(provide
B supporting data in Remarks or on a
g separate sheet)
10 Problematic hydrophytic vegetation*
27 =Total Cover (e�lain)
WOOdV Vine St�uRl (Plot Si2e: 30' ) •Indicators of hydric sdl and wetland hydrology must be
� present,unless disWrbed or problematic
2 y rop c
0 =Total Cover �e9��on
present? N
Remarks:(InGude photo numbers here or on a separate sheet)
US Amy Corps of Engineers Midwest Region
SOIL Sampling Point: SP 2-1a Up
Proflle DescripUon: (Describe to the depth needed to dceument the Indicator or confirtn the absence of indicators.)
Depth Matrix Redox Features
(Inches) Color(moist) % Color(moist) % Type" Loc** Texture Remarks
3 10YR 2/1 100 Loam Organic matter
24 10YR 2/1 100 Loam
30 10YR 2/1 20 10YR 6/2 80 D M Clay loam
'Type:C=Concentration,D=Depletion,RM=Reduced Matrix,MS=Masked Sand Grains. "Location:PL=Pore Lining,M=MaUix
Hydric Soil Indicators: Indicators for Problemat3c Hydric Soils:
Histisol(A1) Sandy Gleyed Matrix(S4) Coast Preirie Redox(A16)(LRR K,L,R)
Histic Epipedon(AZ) Sandy Redox(S5) Dark Surface(S7)(LRR K,L)
Black Histic(A3) SUipped 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)
Stratfied Layers(AS) Loamy Gleyed Matriu(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(FS) hydrology must be present,unless disturbed or
— — problematic
RestricNve Layer(if observed):
Type: Hydric soii presentT Y
Depth(inches):
Remarks:
HYDROLOGY
WeUand Hydrology Indicators:
Primarv Indicators(minimum of one is reauired�check all that aealv) econd Indicators minim m of two re uired
Surface Water(A1) Aquadc Fauna(613) Surtace Soil Crecks(BB)
High Water Table(A2) True Aquatic Plants(614) Drainage Pattems(B10)
Saturation(A3) Hydrogen Sulfide Odor(C1) Dry-Season Water Table(C2)
Water Marks(61) Oxidized Rhizospheres on Living Roots Crayflsh Burtows(CB)
Sediment Deposits(82) (C3) Saturation Vsible on Aerial Imagery(C9)
Drift Deposits(B3) Presence of Reduced Iron(C4) Stunted or Stressed Plants(D1)
Algal Mat or Crust(84) Recent Iron Reduction in Tilled Soils Geomorphic Position(D2)
Iron Deposits(85) (C6) _FAC-Neutrel Test(D5)
Inundation vsible on Aerial Imagery(B7) Thin Muck Surface(C�
Sparsely Vegetated Concave Surtace(88) Gauge or Well Data(D8)
Water-Stained Leaves(89) Other(Explain in Remarks)
e ervabons:
Surface water present? Yes No X Depth(inches):
Water table present? Yes No —$�Depth(inches): Indicators of wetland
Saturation present? Yes No X Depth(inches): hydrology present4 N
(inGudes capillary fringe)
Describe recorded data(stream gauge,monitoring well,aerial photos,previous inspections),'rf available:
emarks:
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 (FACV�—Usually occur in wetlands (estimated probabiliry 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 (LTPL)—Occur in wetlands in another region, but occur almost always
(estimated probability >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
GLENCOE SERIES
The Glencoe series consists of very deep,very poorly drained soils that formed in loamy sediments from
glacial till on glacial moraines.These soils have moderate or moderately slow permeability.Slopes are 0 to
1 percent.Mean annual precipitation is about 28 inches.Mean annual temperature is about 48 degrees F.
TAXONOMIC CLASS: Fine-loamy, mixed, superactive,mesic Cumulic Endoaquolls
TYPICAL PEDON: Glencoe clay loam with a concave slope of less than 1 percent in a
depression on a ground moraine in cultivated field. (Colors are for moist soil unless
otherwise noted.)
Ap--O to 10 inches; black(N 2/0) clay loam; massive; friable; about 2 percent gravel;
cloddy; neutral; abrupt smooth boundary.
A--10 to 24 inches; black(N 2/0) clay loam; weak fine subangular blocky structure;
friable; about 2 percent gravel; neutral; clear wavy boundary. (Combined thickness of A
horizon is 16 to 32 inches.)
ABg--24 to 35 inches; very dark gray (SY 3/1) clay loam;weak fine subangular blocky
structure; friable; few tongues of dark olive gray(SY 3/2)and olive gray(SY 4/2); about
2 percent gravel; neutral; gradual irregular boundary. (0 to 26 inches thick)
Bg--35 to 48 inches; olive gray(SY 4/2) loam;moderate coarse subangular blocky
structure; friable: few tongues of very dark gray(SY 3/1); about 5 percent gravel;
common fine prominent light olive brown(2.SY 5/4)and common medium prominent
strong brown(7.SYR 5/6)Fe concentrations; neutral; gradual wavy boundary. (0 to 30
inches thick)
Cg--48 to 60 inches; grayish brown (2.SY 5/2) loam; massive; friable; about 5 percent
gravel; many medium distinct light olive brown (2.SY 5/4)Fe concentrations; strongly
effervescent; slightly alkaline.
TYPE LOCATION: Steele County, Minnesota; about 5 miles northwest of Owatonna;
2,640 feet south, 2,660 feet west of the northeast corner of sec. 24, T. 108 N., R. 21 W.;
USGS Medford West quadrangle; lat. 44 degrees 8 minutes 46 seconds N. and long. 93
degrees 17 minutes 45 seconds W.,NAD27.
RANGE IN CHARACTERISTICS: Depth to free carbonates is 30 to 60 inches or
more. The Ap in a few pedons will have small amounts of free carbonates. The thickness
of the mollic epipedon ranges from 24 to 80 inches. The control section averages between
22 and 35 percent clay and from 15 to 30 percent fine sand and coarser. Rock fragments
of mixed lithology comprise 0 to 5 percent of the volume of the A and B horizons and 2
to 8 percent of the C horizon. Some pedons have an 0 horizon up to 6 inches in thickness.
A stratified substratum phase is recognized with silt loam, sand, sandy loam, and loamy
sand textures below 40inches.
The Ap or A horizon has hue of lOYR to SY or neutral,value of 2 or 3, and chroma of 0
or 1. It is clay loam, silty clay loam, or loam with 25 to 35 percent clay. Ponded phases
may have mucky modifiers. It is commonly neutral but ranges from slightly alkaline to
slightly acid.
AB horizon has colors and textures similar to the A and Bg horizons.
The Bg horizon has hue of SY or 2.SY, value of 2 to 5, and chroma of 1 or 2. Dark
colored tongues from the A horizon range from few to common. It is loam, clay loam or
silty clay loam. Near the center of some depressions, some pedons have B horizons that
have a slight clay increase relative to the A horizons. It is neutral to slightly alkaline, but
in some pedons the lower part of the B horizon is slightly alkaline with slight
effervescence. The Bg horizon is absent in some pedons.
The Cg horizon has hue of SY or 2.SY, value of 4 to 6, and chroma of 1 to 4. It is loam,
clay loam or silty clay loam. It is slightly alkaline, with weak or strong effervescence.
Calcium carbonate segregations are present in some pedons.
COMPETING SERIES: These are the Coland, Comfrev, Delft, Gielow, James Can,�,
Keddie, Kimmerlin�, Konner, McClave, Peoh, Romnell, Shandep, and Wenas series.
Coland and Comfrey soils do not have rock fragments in their control sections. In
addition, Coland soils are deeper to free carbonates. Delft soils are poorly drained, are not
in closed depressions, have prismatic structure in subsoil, and do not have tongues of the
A horizon in the Bg horizon. Gielow, James Canyon, Keddie, Kimmerling, Konner,
McClave, Peoh, and Wenas soils are drier in the soil moisture control section during the
120 days following the summer solstice. Romnell soils contain appreciable amounts of
gypsum in their sola. Shandep soils do not have tongues of A horizon in the Bg horizon
and have a coarse textured 2C horizon.
GEOGRAPHIC SETTING: Glencoe soils typically are in closed depressions or low
gradient swales within the Des Moines lobe of the Late Wisconsinan glaciation. The
Glencoe soils are formed in loamy colluvial sediments and loamy glacial till. Mean
annual temperature ranges from 45 to 52 degrees F. Mean annual precipitation ranges
from 25 to 32 inches. The frost free days range from 124 to 172. The elevation above sea
level range from 700 to 1600 feet.
GEOGRAPHICALLY ASSOCIATED SOILS: These are the Canisteo, Clarion, Harps,
Nicollet, and Webster soils. The well drained Clarion soils are on the sloping uplands.
Somewhat poorly drained Nicollet and the poorly drained Canisteo, Webster, and Harps
soils are on nearly level to gently undulating slopes. All the above have mollic epipedons
less than 24 inches thick. In addition, the Canisteo and Harps soils contain free
carbonates throughout. The Glencoe soils also are associated with the Hayden and Lester
soils and their respective topographic associates in some places.
DRAINAGE AND PERMEABILITY: Very poorly drained. Surface runoff is
negligible. Permeability is moderate or moderately slow.
USE AND VEGETATION: Mostly drained and cropped to corn and soybeans. Native
vegetation was a wet site plant community of the tall grass prairie plant formation.
DISTRIBUTION AND EXTENT: South-central Minnesota and possibly north-central
Iowa. Large extent.
MLRA OFFICE RESPONSIBLE: St. Paul, Minnesota
SERIES ESTABLISHED: Dakota County, Minnesota, 1945.
REMARKS: Diagnostic horizons and features recognized in this pedon are: mollic
epipedon-the zone from the surface to a depth of 35 inches(Ap,A, and ABg horizons);
cumulic subgroup-mollic epipedon is more than 24 inches thick; aquic moisture regime-
low chroma immediately below the A horizons.
HAMEL SERIES
The Hamel series consists of very deep,poorly drained and somewhat poorly drained soils that formed in
slope colluvium and glacial till on moraines.T'hese soils have moderately slow permeability.Their slopes
range from 1 to 4 percent.Mean annual precipitation is about 28 inches.Mean annual air temperature is
about 47 degrees F.
TAXONOMIC CLASS: Fine-loamy,mixed, superactive, mesic Typic Argiaquolls
TYPICAL PEDON: Hamel loam with a 2 percent concave slope on a glacial moraine in
a cultivated field. (Colors are for moist soil unless otherwise noted.)
Ap--O to 10 inches;black(lOYR 2/1) loam,very dark brown (lOYR 2/2)dry; weak very
fine subangular blocky structure; friable; common very fine roots; about 1 percent gravel;
neutral; abrupt smooth boundary.
A--10 to 16 inches; black(lOYR 2/1) loam,very dark gray(lOYR 3/1) dry; weak very
fine subangular blocky structure; friable; common very fine roots; about 4 percent gravel;
neutral; gradual smooth boundary. (Combined thickness of A horizon is 14 to 30 inches.)
AB--16 to 24 inches; very dark gray(lOYR 3/1)clay loam, dark grayish brown(lOYR
4/2) dry; many fine prominent brown(7.SYR 4/4) Fe concentrations; moderate fine
angular blocky structure; friable; common very fine roots; about 4 percent gravel; neutral;
gradual wavy boundary. (0 to 10 inches thick.)
Btgl--24 to 40 inches;very dark grayish brown (2.SY 3/2)clay loam, grayish brown
(lOYR 5/2) dry; many fine prominent brown(7.SYR 4/4)Fe concentrations;moderate
medium prismatic structure; friable; few black(lOYR 2/1)clay films on faces of peds;
about 5 percent gravel; neutral; gradual wavy boundary.
Btg2--40 to 46 inches; dark grayish brown (2.SY 4/2) clay loam; many coarse prominent
brown(7.SYR 4/4) Fe concentrations;moderate medium subangular blocky structure;
friable; few black(l 0YR 2/1) clay films on faces of peds; about 4 percent gravel; neutral;
clear wavy boundary. (Combined thickness of Btg horizons is 12 to 30 inches.)
Cg1--46 to 55 inches; olive gray(SY 5/2) loam; many medium prominent yellowish
brown(lOYR 5/6)Fe concentrations; massive; friable; about 3 percent gravel; slightly
effervescent; slightly alkaline; gradual wavy boundary.
Cg2--55 to 80 inches; olive gray(SY 5/2) loam; many medium prominent yellowish
brown(lOYR 5/6)Fe concentrations; massive; friable; about 4 percent gravel; slightly
effervescent; slightly alkaline.
TYPE LOCATION: Wright County,Minnesota; about 1.5 miles southwest of Silver
Creek, 1200 feet south and 2300 feet west of the northeast corner of Sec. 18, T.121 N.,
R.26 W., USGS Annandale quadrangle; lat. 45 degrees 17 minutes 34 seconds N.; long.
94 degrees 00 minutes 13 seconds W.,NAD27
RANGE IN CHARACTERISTICS: Depth to free carbonates range from 30 to 65
inches. The mollic epipedon thickness ranges from 24 to 60 inches. Typically the upper
colluvim contains less than 2 percent gravel by volume and the lower part contains 2 to 6
percent gravel by volume of mixed lithology.
The A horizons have hue of lOYR or is neutral, value of 2 or 3, and chroma of 0 to 2.
Typically it is loam or clay loam, but silt loam or silty clay loam are within the range. It
has coatings of clean sand and silt particles in the lower part of the A horizon in some
pedons. It is moderately acid to neutral.
The Btg horizon has hue of lOYR, 2.SY, or SY, value of 2 to 4, and chroma of 1 or 2. It is
clay loam, silty clay loam high in sand, or loam. It has between 25 and 35 percent clay
and 15 to 35 percent fine sand and coarser. It has B/A clay ratios of 1.2 to 1.4. It has few
to many, faint to prominent clay films. It is moderately acid to neutral.
The C horizon has hue of a 2.SY or SY, value of 4 to 6, chroma of 1 or 2. It is loam or
clay loam. It is slightly alkaline or moderately alkaline. The clay content ranges from 18
to 32 percent and the total sand content ranges from 25 to 45 percent.
COMPETING SERIES: These are the Alvada, Barry, Berville, Brookston,
Buntingville, Clackamas, Cordova, Forestcity, Jameston, Maren�o, Mill r�,Navan,
Nosoni, Rensselaer, and Westland soils. The Alvada series (Tentative - OH) is not in the
OSD file at this time. The Barry, Berville, Brookston, Cordova, Marengo, Millgrove,
Navan, Rensselaer, and Westland soils have a mollic epipedon that is less than 24 inches
thick. The Buntingville soils have carbonates at depths of less than 20 inches. The
Clackamas and Nosoni soils lack free carbonates in the series control section.
The Forestcity soils have 45 to 65 percent sand and 10 to 18 percent clay in the
underlying material. The Jamestown soils formed in a firm and very firm till associated
with the Iowan Erosional surface.
GEOGRAPHIC SETTING: Hamel soils have concave slopes in swales, rims of closed
depressions, foot and toe slopes, and upper drainageways below sloping to very steep
slopes. Slope gradients are 1 to 4 percent. Hamel soils formed in slope colluvium and
glacial till of Late Wisconsinan Age. Mean annual air temperature is about 45 to 48
degrees F. Mean annual precipitation is about 25 to 30 inches. Frost free days range from
125 to 165. Elevation above sea level ranges from 700 to 1600 feet.
GEOGRAPHICALLY ASSOCIATED SOILS: These are principally the Ha•�and
l.ester soils. These soils are well drained and are on the higher lying, gently sloping to
very steep slopes.
DRAINAGE AND PERMEABILITY: Poorly drained and somewhat poorly drained.
Surface runoff is low or moderately low. Permeability is moderately slow. The apparent
seasonal high water table is at .5 to 1.5 feet for the poorly drained phase and 1.5 to 2.5
feet for the somewhat poorly drained phase during spring in normal years.
USE AND VEGETATION: Most of this soil is cropped to corn, hay, soybeans, and
small grains. However, significant areas are in pasture and forest. Native vegetation is
mixed wet prairie grasses and deciduous forest.
DISTRIBUTION AND EXTENT: Primarily in the southeast one-quarter of Minnesota
in the timbered, hilly, "gray" till region. Moderately extensive.
MLRA OFFICE RESPONSIBLE: St. Paul,Minnesota
SERIES ESTABLISHED: Hennepin County, Minnesota, 1969.
REMARKS: Diagnostic horizons and features recognized in this pedon are: mollic
epipedon-the zone from the surface to a depth of 40 inches (Ap, A,AB and Btg 1);
argillic horizon -the zone from 24 to 46 inches(Btgl, Btg2,). Type location moved from
Hennepin County, Mn. to Wright County, Mn., 11/96 to better exemplify the series
concept.
A somewhat poorly drained overwash phase is recognized that has 8 to 20 inches of
colluvium over the original dark colored surface.
ADDITIONAL DATA: Refer to MAES Central File Code No. 785 for results of some
laboratory analysis of this series.
KLOSSNER SERIES
The Klossner series consists of very deep,very poorly drained soils formed in well decomposed organic
material 16 to 50 inches thick overlying loamy deposits on moraines,till plains,lake plains,flood plains,
and hillside seep areas.They have moderately slow to moderately rapid permeability in the organic
material,and moderate or moderately slow permeability in the loamy material.Slopes range from 0 to 8
percent.Mean annual precipitation is about 28 inches.Mean annual temperature is about 47 degrees F.
TAXONOMIC CLASS: Loamy,mixed, euic, mesic Terric Haplosaprists
TYPICAL PEDON: Klossner muck-with a 1 percent 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 gray(lOYR 3/1)dry; about 20
percent fiber, less than 5 percent rubbed; weak fine subangular blocky structure; very
friable; many very fine roots; moderately acid; abrupt smooth boundary.
Oa--10 to 26 inches; black(lOYR 2/1)muck, dark gray(lOYR 4/1) dry; about 60 percent
fiber, about 6 percent rubbed; weak fine subangular blocky structure;very friable; many
very fine roots; moderately acid; gradual smooth boundary. (Combined thickness of O
horizon is 16 to 50 inches.)
2A1--26 to 36 inches; black(N 2/0)mucky silty clay loam; weak medium subangular
blocky structure; friable; few very fine roots; slightly acid; gradual smooth boundary.
2A2--36 to 48 inches; black(N 2/0) silty clay loam; massive; friable; few dark reddish
brown(SYR 3/4) iron oxide concentrations in root channels; about 1 percent gravel;
neutral; gradual wavy boundary. (Combined thickness of 2A horizon is 8 to 45 inches
thick.)
2Cg1--48 to 65 inches; olive gray(SY 5/2)clay loam; massive; friable; dark reddish
brown(SYR 3/4)Fe oxide concentrations in root channels; many medium prominent
yellowish brown (lOYR 5/6)Fe concentrations; about 1 percent gravel; slightly
effervescent; slightly alkaline; gradual wavy bounday.
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(lOYR 5/4) Fe concentrations; about 3
percent gravel; slightly effervescent; slightly alkaline.
TYPE LOCATION: Nicollet County,Minnesota; 2600 feet north and 2300 feet east of
the southwest corner, sec. 12, T. 110 N., R. 28 W.;USGS Nicollet quadrangle; lat. 44
degrees 20 minutes 53 seconds N. and long. 94 degrees 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 herbaceous plants. The organic matter
content ranges from 25 to 60 percent in the organic surface and 5 to 20 percent in the 2A
horizon. The reaction of the organic material ranges from moderately acid to slightly
alkaline. Some organic layers contain free carbonates.
The O horizon has hue of l OYR, SYR, or is neutral, value of 2 or 3 and chroma of 0 to 2.
It is dominantly muck(sapric material) however, some pedons have thin layers of hemic
material, less than 10 inches thick.
Some pedons have highly organic mineral plow layers.
The 2A horizon has hue of lOYR, 2.SY, SY or is neutral, value of 2 or 3 and chroma of 0
to 1. It is loam, silt loam, sandy clay loam, silty clay loam, clay loam or mucky modifiers
of these textures. It is moderately acid to slightly alkaline. Some pedons contain thin
layers of coprogenous earth.
The 2Cg horizon has hue of lOYR, 2.SY, SY, SGY, or is neutral, value of 2 to 7 and
chroma of 0 to 2. It is loam, silt loam, silty clay loam, clay loam, sandy clay loam, sandy
loam or fine sandy loam, or their gravelly or cobbly analogues. It is slightly acid to
moderately alkaline. The upper 12 inches of this horizon averages less than 35 percent
clay. Some pedons contain thin strata of fine sand, loamy sand, or silt. Gravel or cobble
sized rock fragments range from 0 to 25 percent by volume. Some pedons contain free
carbonates. Sandy substratum and ponded phases are recognized.
COMPETING SERIES: These are Linwood, Medo, Palms, Philbon and Shalcar series.
Linwood soils have well expressed granular structure to depths of more than 12 inches
and formed mainly in woody fibers. Medo soils have sandy textures in the lower part of
the series control section. Palms soils have organic matter content greater than 75 percent
and do not have an A horizon directly below the organic material. Philbon soils have
fibric and hemic material in the upper 12 inches. Shalcar soils ave less than 26 degrees
difference between mean January and mean July temperatures.
GEOGRAPHIC SETTING: Klossner soils are in basins that were formerly lakes or
ponds, lake plains, till plains, flood plains, or moraines. They are also on hillside seep
areas in moraines and sideslopes of river valleys. Slopes range from 0 to 8 percent. The
soils on nearby uplands are generally loamy. The mean annual temperature ranges from
45 to 50 degrees F. The mean annual precipitation ranges from 24 to 32 inches. Frost free
days range from 110 to 160. Elevations above sea level range from 800 to 1400 feet.
GEOGRAPHICALLY ASSOCIATED SOILS: The main ones are the Canisteo, Hams,
Okoboii, Glencoe, Muske�o and Hou ht�on soils. Canisteo 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 poorly drained. Surface runoff is
negligible. Permeability is moderately slow to moderately 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 or grass sod. Other areas are in
vegetation of grasses, reeds, sedges, alder, aspen, or willow. Some of the hillside seep
areas are set aside as natural areas and called fens.
DISTRIBUTION AND EXTENT: The south central and southeast part of Minnesota
and possibly northern Iowa. The series is extensive.
MLRA OFFICE RESPONSIBLE: St. Paul,Minnesota
SERIES ESTABLISHED:Nicollet County,Minnesota, 1989.
REMARKS: Diagnostic horizons and features recognized are: sapric soil materials from
the surface to about 26 inches; loamy mineral material from 26 to 50 inches or more;
aquic moisture regime. This soil was formerly included in the Palms Series in Minnesota.
ADDITIONAL DATA: Refer to MAES-CFC#'s 2697, 3251, 3400 and 3475.
Photo Lo
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sample point SP 1 -1 Wet. Wetland area comes up to ditch running
through property near this transect.
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Print Form
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l�S:\rmy('orps
of Enginecrs
SL Pxul District
Request for Corps of Engineers Wetland Delineation Review
Please enter the following general information about the property under review:
Name of�n•operty owncr
Bob Angen
Property Address(No. & Street, City, ,State,Zip Code)
835 Hunt Farm Rd, Orono, MN
Lat. � Lon . � decimal de �•ees
Coun � Hennepin
Location: SE 1/4 Section 30 Township 118N Itange 23W
Size of revie�v area 3.5 acrc(s)
f3y submission of this ���etland delineation report I am rcquesting that the U.S. Army Corps of Engineers, St.
Paul UisU'ict provide me with the following (check only one box):
❑ Wetland Delineation Concurrence. Ca�currence with awetland delineation is a written notification trom
thc Corps concurring, not concurring, or commenting on the wetland boundaries delineated on a property.
Under this c•cquest,the Corps will not address the jurisdictional status of the �vetlands on the property,only
the boundaries ot�the resources within the review area.
✓� Peeliminary Jurisdictional Determination. Preliminary J�u•isdictional Determination. A preliminary
jurisdictional determination is a nonbinding written indication d�at there may be waters of the United States,
including wetlands, on a parcel or indications of the approximate location(s)of waters of the United States or
wetlands on a parcel. f�or purposes of computation of impacts and compensatory mitigation requirements a
permit decision made on the basis ofa preliminary jurisdictional dctermination will treat all waters and
wetlands in thc review area as if they �re jurisdictional waters of'the U.S. Preliminary jurisdictional
dcterminations are advisory in natw•e and may not be appealed.
❑ Approved Jurisdictianal Determination. An approved jurisdictional determination is an otfiicial Corps
determination that jurisdictional waters of the United States or navigable waters of the United States, or both,
are either present or absent on the property. An approved jurisdictional determination precisely identities the
limits of those waters on the project site determined to be jurisdictional under the Clean Water Act or Rivers
and Harbors Act. Appi•oved jurisdictional determinations can be relied upon by the affected party for a
period of live years. An approved jurisdictional determination may be appealed through the Corps'
administrative appeal process.
In order for the Corps to process your request, the wetland delineation must be prepared in accordance with
the 1987 Corps of Engineers Wetland Uelineation Manual, any approved Regional Supplements to the 1987
Manual,and the Guidelines for Submitting Wetland l�elineations in Minnesota and Wisconsin
(http://www mv nsace.ai�my.miUce ilatory/� �
Requestor �� � i Date 12-19-13 __
Name (typed)F�anklin J Svobo
• • � • • �
� � • • • � � • � • � • ' � i• � .
1. Project/Site Information
ProjecUSite Name: 835 Hunt Farm Rd Local Government Unit: Orono
Location (address and/or T, R, S@C.�: Lot 1,Blk 3 Huntington Farrn Addn,part of lhe 5E Y.SW%SE Y.Section 3U,T118N,R23W
2. Applicant Information
Applicant Name: Bob Angen Address: PO Box 180
City, State,Zip: Roberts, WI 54023
E-mail: boberta50@msn.com Phone: 612-750-4603
3. Agent/Consultant Information
Company Name {if applicable): svoboda Ecoiogicai Resources Contact Person: Frank Svoboda
Address: 25580 Nelsine Drive City, State, Zip: Shorewood,MN,55331
E-mail: franks@gpsinnovations.com Phone: 952-471-1100
4. Description of Request
Check all that apply: 0 Wetland Boundary (must attach wetland delineation report)
�Wetland Type (Eggers & Reed and/or Circular 39 type)
5. Signature
By signature below, the applicant requests a determination from the Local Government Unit under
Minnesota Rules 8420.0225 on the submitted wetland boundary and type information in this application.
The applicant also affirms that theyy�re the owner of the subject property or have permission from the
landowner to pursue this determin ti0n.
i �
� r 1 / �.:,cI C�`,�. l l ��' �•7 .
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Applicant or Authorized ent ignature Date
Important Notes:
• The applicant may be required to submit multiple copies of the reporUinformation to the
LGU. The LGU may require the applicant to submit copies directly to Technical Evaluation
Panel Members. Check with your LGU regarding their submitta!requirements.
• The �GU decision must be made in compliance with Minnesota Statutes, section 15.99.
For LGU use only
Date Received:
Page 1 ot 1
BWSR Wetland Boundary/Type Applicaiion Form 11��fl�08