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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 FIGURES -s • s ,� -'r ( • S. • /Q � ,r � . . n ! — -ir \ •' �� ,'. •,�! � • / y ` ,�.,3 •M• • t .. �1. , � • � � � •� .�- .�._ .., ti- ' . � � \� � � '�� �� � � 1• ' _-,_... __ i � -� � � . r ..� > ...�.. � ' O I .� �^.�" /"Y� .�._ S '� 1 • . ._ • j. . , • ,• • �M` • • �;.��� � � .. `` • L�"� 1 � • y i ! ��. ,,� _ �36 F ,��,�,__�-�.� ..� ;.�•�-� - � �� 31 a . . Q , - 1. ��. , t �. .�� •�� • �� J'''.... "u' ..�`., "'"'�v%'�. .. _ '•• . 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'S _ � A �, _ 4'" � SOI IS y,,y � . � s LS.�J� • 1 i ���� T/� �. , �, e � ,�, '1� 4 ' �` �:�:� ��� Hydric � - � . � • - ~ e � � ,�. � �'� �, ��` �,� � � � ' '� � artiall h dric ����,.,��� ��,��:������.���,� ;a,�b,�,s ,«, _ � P Y Y '����: �F r � '���,3a�?� .,�3��,�``�.;�:��a�" '`"r,��.�� � .� Predominantly nonhydric f I�,�� �� y� �.���y. 6��1 1 � � � / �� 4��j'.:, �^ '.� ` �t I " ?�' ':�-'`� �"�' Approximate Wetland Boundary and Soils Figure 6 Overlaid on 2012 Aerial Photo .!f���SVQ BO DA 0 165 330 660 4565 Ba�Side Rd � �� s rces � FPA+ y Ecological Re ou 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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'ru,;,�%,� • �a,� ���, y � #'�q oF` IJ ''t t lf�� .�1�► r� 'Y� 'f�r '/ 5%-�� �� ,LZ, .:'t,,. �:, - i ����:, �,�i� iQ �`�,�, �S%1p ��j �i,��.� 's �-�Yi'�nrl'X#1 �� .d. ;r� r ��',Y�' .� T� �:, ���.,r.is:i + � �� �� M �1����f.�.'a�'Fti�� �.�r r.d-Jui' . , �� r ' � .„'� s . � . . . � , , . .. . � �'_ �.L7�.L .1��1J,1� ` y� � J.+_s,. i.�9a �L',I�f_��a.__ tYh1�.�:._�Z ...�� . - +�.:r!. W.... ��1�1; �-�� �, . _.,M. _ 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 �� ..� ����� J � � �� I ���� � '.. �' R .- r� .� 7�1,���dS�+_ �t �e. � '_� - '� �'i r y � -il�pr�,�, .., ��,,.M �,�:;. .i� 4�,y„�'� ��t �� . _ � �. , ,k,,.`%n,:� . � � � '„► �`�"y,-. {� ;'� ��H�y �'�%`�F �� , °��� ,�;�, `-�t�=" ,��' � : , � .. , .� r� .�, � t�p� �r; , ��w. ���' _ ���, ,�����fF�i��f �Y�: "�� `�w� ��r�� ,���� 1� � .�'ry ,�'�,�5, _�� � ����'��— ad.��M���z���� �s� '�y- e ` �he� t.�� " . '�=`` ,. ..��. ,�_� _`,t �,�t�y� - � P � � � rst�..� ��t � .. :���^`R,t'�t��- r � � � '17�t � ti� ��.,� ���I�] F�.: ' �t�^�"t ��s�r.� ', '., .�. + ,��1` '�' �' I ���'�`�� ��f�� 'z � • ���'� _ � '� ����� �• ���r�'' ¢'F E�„ i� �'� - _ � ���`�.'i� 3�� ' �,�� , f s �0��: r.,e'���'� ��. � ��P ' ��-"��.n �� ~� '.���r ��' � - 'L � ��t C 7�`- � �� � � � .. . c� � y+,4 �? r, 7% _"�����'y:�'#���d �c%-� ��.' �,, '�p rs. ' �!. ,rf�. ��- q..� _ i ', . -rt . � � t��M1 '��� �� � ;� f ~ � w �`p � .fa � ;� ��� J�' �t.�, , ` . .��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. 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T117N R23W S06 Overview Figure i Overlaid on Topographic Map .�+��svoBooA Zo14_o22 � � 0 1,250 2,500 5,000 4565 Bayside Rd �- ��� EcoloQical RescxircPs FCCt 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. �.��_ � �-�, ., �� ,�,- ,•�, � ��� :� . r�� �-- _ �: .�� �Ayd � �,r� ' r� ; _ �a. �. 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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 r� "'� �"�'_ `�` "'•► � � / ,I � �O „r $' _..— . .. � ,� �' ',�� i • " � . • i . . . '�"'ti � � , . • j_ _ � ... �! , . , �• t'_---•�__ - • � ' t `� � Q ( ��.,,�:: � – �._�',r�.. � - �.., . • e �`� ` � . ' '� � ., - • j� t ` � �� � � � � �.�,__�. � ,.�'°"' `"`�,.�... �� �" . `' � • - �� cr1�. Q, ! '. " % �! � .w � �,� � / ``� • • , �..�0 , ��N� ..__�,i_ � �► ' + .•�, . _ �`y � . �.! . � �r` `'•� � `..�°' +�w ....�.+l� �,.��.. ,,,�, —� # ' �.. '� ``"i �•�••-�i�� ��� . , `� • . ,._ . �� � , - - � � � . _� ... � � `� _ - _ . � ' 1 ''� -�' � ' -:'�- `� . 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