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Wetland Delineation-2016
' � � � • • � . . • � . • • • � ' • . � � • • - • . REPORT FOR: FROM: Todd Holmers Travis Fristed Casco Ventures LLC Environmental Services Manager 16192 Highway 7 7900 International Drive, Suite 550 Excelsior, MN 55331 Minneapolis, MN 55425 612.991.9777 952.426.0699 toddholmers@gmail.com travis.fristedC�is-grp.com �I I� • '� . . . . ,. „,_. c"`.�:`��'�x�`T'.�.�,�'�' , , � �::' . � I=dy r z' � �°,-°`�}s.�,.,t :&��--��:.„�`�'.,-:�3����. 3..,�z1.� ,,K g"rt. T� 4! r- ''`:- ^�",r,!T��l�'� ExecutiveSummary ................................................................................................................. 1 ProjectDescription................................................................................................................... 1 Definitions + Methodology ........................................................................................................ 2 Find i ngs.................................................................................................................................. 5 Recommendations.................................................................................................................... 7 Data Sources + Literature Cited................................................................................................. 8 Table 1. Vegetation Indicator Status........................................................................................... 3 Table 2. Delineated Wetland Summary ....................................................................................... 6 :: � s � � � � .. Appendix A: Figure 1. Project Location....................................................................................... A Figure 2. DNR Public Waters Inventory and National Wetlands Inventory Figure 3. Soil Survey of Hennepin County Figure 4. LiDAR Elevations & Hillshade Figure 5. Aerial Photograph Appendix B: Figure 6. Wetland Delineation Map.......................................................................... B Wetland Delineation Data Forms Appendix C: Antecedent Precipitation Data................................................................................. C Photo Log Appendix D: Joint Application Form for Activities Affecting Water Resources in Minnesota ................ D 2525 Shadywood Road Page i Certification 2525, 2535, AND 2545 SHADYWOOD ROAD LEVEL 2 WETLAND DELINEATION Section 20, T117N, R23W City of Orono, Hennepin County, Minnesota I hereby certify the above-described routine on-site Level 2 wetland delineation was performed on May 3, 2016. The wetland delineation meets standards and criteria specified in the Regional Supplement to the Corps of Engineers Wetland Delineation Manual: Midwest Region. �zC/2��"�- Lucas Mueller Environmental Scientist I hereby certify the quality assurance review of this wetland delineation report was completed by me or under my direct supervision, and that I am a Certified Wetland Delineator in the State of Minnesota. Travis Fristed, PWS (#2360), MN WDC (#1169) Senior Environmental Scientist/Environmental Services Group Manager 2525 Shadywood Road Page ii Executive Summary ISG completed a wetland investigation within a 3.66 acre project area on May 3, 2016 (as shown on the attached Figures) for future development. The project is located at 2525, 2535, and 2545 Shadywood in Orono, Minnesota. This wetland investigation was performed in accordance with the 1987 US Army Corps of Engineers Wetland Delineation Manual and the 2010 Midwest Regional Supplement, and all applicable supporting documents for areas meeting wetland criteria for a routine wetland delineation in accordance to the MN Wetland Conservation Act and the US Army Corps of Engineers Section 404 Program. Vegetation, soil and hydrology sampling have been completed on all potential wetland areas within the project area. Wetland determinations were based on the three required technical criteria: occurrence of hydric soil, predominance of hydrophytic vegetation, and the presence of one primary and/or two secondary indicators of wetland hydrology. Potential wetland areas (mapped hydric soils, NWI signatures, and low depressional areas) were investigated on-site and delineated as upland. One (1) wetland was delineated during the field investigation. The delineated wetland was a Type 3 Shallow Marsh. Adjacent upland area was forested rolling hills to the north, Kelly Road to the south, additional wetland to the west, and residential homes to the east. Project Description TRiTRC�7UC�TIO��.' ISG was retained to identify and delineate all wetland areas that exist within the project boundary. The wetland investigation area (project area) encompasses three parcels totaling 3.66 acres at 2525, 2535, and 2545 Shadywood Road, in Orono, Minnesota. The purpose of the wetland investigation is to accurately identify wetland areas onsite so that they can be incorporated into future plans for the development of the property. This report is intended to facilitate any regulatory discussions of Wetland Conservation Act and Clean Water Act Section 10/404 permitting for this project. I t...,, `;-� x���I The project area is located at 2525, 2535, and 2545 Shadywood Road in Section 20, T117N, R23W, in the city of Orono, Minnesota (See Appendix A for a location map). The site is located within an Unknown minor watershed (20118) and the Mississippi River— Twin Cities major watershed (20). The topography of the site ranges in elevation from approximately 928'to 952'above msl. At the time of this delineation, 2525 Shadywood Road Page 1 the investigation area was composed of rolling forests in the northeast area, which sloped southwest into a wetland complex. The project site is located in a moderately spaced residential landscape near Lake Minnetonka in the city of Orono. The investigation area is located southwest of Shadywood Road (CSAH 19), west of Lydiar Avenue and northeast of Kelly Avenue. Definitions + Methodology This investigation was performed in accordance with the US Army Corps of Engineers 1987 Wetland Delineation Manual and the 2010 Midwest Regional Supplement, and all applicable supporting documents for areas meeting wetland criteria for a routine wetland delineation in accordance to the Minnesota Wetland Conservation Act and the US Army Corps of Engineers Section 404 Program. The following definitions, diagnostic environmental characteristics, and the methodology used is based on the mandatory technical criteria for the identification and delineation of wetlands. As defined in 33 CFR Part 328, Section 3,the term wetlands is defined as: Those areas that are inundated or saturated by surface or ground water at a frequency and duration sufficient to support, and that under normal circumstances do support, a prevalence of vegetation typically adapted for life in saturated soil conditions. The frequency and duration of saturation may vary by geographical region, and is largely dependent upon climatic conditions. Wetlands generally include swamps, marshes, bogs, and similar areas. Wetlands have the following general diagnostic environmental characteristics: Hydrophytic Vegetation The wetland vegetation criterion is satisfied when the prevalent vegetation consists of plant species adapted to inundation or substrates periodically deficient in oxygen as a result of prolonged saturation. Specifically, this includes plant communities that under normal circumstances have more than 50% of the composition of the dominant species from all strata ranked with an indicator status as obligate wetland (OBL), facultative wetland (FACW), and/or facultative (FAC) species. The indicator status for individual plants as defined by the updated 2016 Minnesota National Wetland Plant List are identified and described in the following table: . ;�>� 2525 Shadywood Road Page 2 Tab/e 1. Vegetation Indicator Categories . . . -. . • • Obligate(OBL) Almost always Facultative Wetland(FACV1� Usually Facultative(FAC) Equally likely to occur in uplands Facultative Upland(FACU) Rarely Upland(UPL) Almost never Hydric Soil A hydric soil is a soil formed under conditions of saturation, flooding, or ponding long enough during the growing season to develop anaerobic conditions in the upper part. Examples of hydric soil indicators include: the accumulation of organic matter, low-chroma soil matrices, gleying, redox concentrations, redox depletions, and hydrogen sulfide odor. Wetland Hydrology According to the 1987 manual, wetland hydrology is present when the area is inundated either permanently or periodically at mean water depths less than or equal to 6.6 feet, or the soil is saturated to the surface at some time during the growing season. The Midwest Regional Supplement requires fourteen (14) or more consecutive days of flooding or ponding, or a water table of twelve (12) inches (30 cm) or less below the soil surface, during the growing season at a minimum frequency of five (5) years in ten (10) (50% or higher probability) to satisfy wetland hydrology. � The wetland hydrology criterion can be satisfied with observation of one (1) primary hydrology indicator or two (2) secondary hydrology indicators. Potential primary indicators of wetland hydrology may include, but are not limited to: inundation, saturation, water marks, drift lines, sediment deposits, and a thin muck surface. Potential secondary indicators of wetland hydrology may include, but are not limited to: surface soil cracks, drainage patters, saturation visible on aerial imagery, and the FAC-neutral test. , r- f14�`, �'�t/L �� � 1�^\• i- �'�1 J t, l_�. �, Map Review Prior to fieldwork, several mapping sources were consulted to identify potential wetland habitats. The sources consulted include the United States Fish and Wildlife Service (USFWS) National Wetland Inventory (NWI), United States Department of Agriculture (USDA) Natural Resources Conservation Service (NRCS), formerly Soil Conservation Service (SCS) Soil Survey, Minnesota Department of Natural Resources (DNR) Public Waters Inventory (PWI), and United States Geological Survey (USGS)Topographic maps. Areas indicating evidence of potential wetland conditions were evaluated in greater detail through fieldwork. 2525 Shadywood Road Page 3 Precipitation Data Analysis Precipitation data from the Minnesota Climatology Working Group and Natural Resources Conservation Service WETS Tables were used in conjunction with the NRCS Method for Evaluating Antecedent Moisture Conditions to determine precipitation conditions under which the investigation was conducted. ,� Field Sampling Procedures Sample transects were established in representative transition zones between wetland and upland for each observed plant community. For potential wetland areas greater than five acres in size, a minimum of three transects were established along the baseline wetland boundary for lengths of up to one mile, three to five transects for one to two miles, five to eight transects for two to four miles, and eight or more transects for wetland baseline boundaries that exceed four miles in length. Transect intervals do not exceed 0.5 mile apart for each other. Transects are comprised of two sample points, one sample in upland and one sample point in wetland. A field data sheet was completed describing the dominant soil characteristics (to a minimum of 24 inches below the soil surface), plant communities, and hydrology indicators at the sample point. The presence of water was observed after time (depending on soil characteristics) was allowed for movement of water through the soil substrate. Absolute percent areal cover was recorded for the species that were observed (which may exceed 100% total area due to overlap) and dominance was determined by using the 50/20 rule. Vegetation was sampled within each stratum present at a sample point using the following circular plot sizes: • Trees - 30 ft radius • Saplings and Shrubs - 15 ft radius • Herbaceous - 5 ft radius • Woody Vines - 30 ft radius The sample points were marked with 4-foot lathe, photographed, and flagged with surveyor's tape (if not within an agricultural land use). Other samples were taken at unmarked locations to provide verification of the wetland edge, as needed. Wetland Boundary Delineation The wetland boundaries were determined using changes in topography, dominance of hydrophytic/non-hydrophytic vegetation, hydric soil indicators, and/or hydrology characteristics. Wetland edges were marked with pink "wetland delineation"flags. The wetland edge is considered 2525 Shadywood Road Page 4 to be the highest extent of the wetland basin. Areas below the flagged edge satisfy the three required wetland criteria while areas above were lacking in one or more of these criteria. US Army Corps of Engineers Regulatory Guidance Letter 90-6 requires documentation sufficient to allow a reasonably accurate replication of the delineation at a future date. Reasonably accurate is defined as within 0-2 meters accuracy. Precise positions of sample points and the wetland edge have been located by a sub-meter GPS unit and have been included in the wetland delineation drawing or map for this property. Wetland Type Classification Wetlands were classified using Wetland P/ants and P/ant Communities of Minnesota and Wisconsin (Eggers & Reed 2007), Classification of Wet/ands and Deepwater Habitats of the United States (Cowardin, et al, 1979) and Wet/ands of the United States (Fish and Wildlife Service Circular 39, Shaw and Fredine 1971). Findings M�P REV?E4�� The NWI map lists three (3) NWI signatures in the western and southern half of the project area. The northern most basin is listed as a Freshwater Emergent Shallow marsh wetland (PEM1C). The central basin is listed as a Freshwater Forested/Shrub wetland (PSS1C). The southernmost basin is listed as a Freshwater Pond Deep Marsh wetland (PABG). The basin complexes are shown in Figure 2, Appendix A. Soils within the project area have been mapped by the NRCS along with their hydric classification. The soils within the project area consist mostly of Houghton and Muskego soils, with the northern tip consisting of Lester loam. The location of each soil unit occurring within the project boundary is shown on the Hennepin County Soil Survey map (Figure 3, Appendix A). There is no DNR Public Water watercourse located within the project area. Minnetonka-Upper Lake is located 530 feet south and west of the project boundary and across Kelly Avenue. The lake is mapped as a DNR PWI as well as a NWI Shallow Open Water Community Lake (L2UBH) (Figure 2, Appendix A). The LiDAR map (Figure 4, Appendix B) illustrates elevations varying within the project boundary, ranging from 928 feet above msl in the south to 952 feet above msl in the north portion of the project area. The precipitation received in the project area during the previous three months was within the wet range (70-100th percentile) for this area. Prior to the sample date of May 3, 2016, there was normal precipitation in March, and wet precipitation in April and February. Therefore the field work was 2525 Shadywood Road Page 5 completed under wet conditions according to the precipitation worksheet for wetland delineations (Appendix C). Based on the data reviewed and fieldwork conducted, one (1) area was examined for wetland characteristics within the project area. One (1) wetland was ultimately delineated and is further described within this report. The delineated wetland is identified as Wetland A, which includes sample points 1-4. Field data forms for each sample point are located in Appendix B. Refer to Figure 5 (Appendix B) for a map of the project boundary, wetland basins, sampling transects, and area. Photos of the wetland basin within the project area are included in Appendix C. � � : � _ . ,_ The prominent aquatic resource adjacent to the project boundary is Minnetonka-Upper Lake, located 530 feet south and west of the project boundary and across Kelly Avenue. The lake is mapped as a DNR PWI as well as a NWI Shallow Open Water Community Lake (L2UBH). Table 2. Delineated Wetland Summary i � � � � � � � � � �• � � � : � ��� � •� , � , � , � , , ; � .., . ., ' '� = : : � -- • � Type Shallow Marsh ��32 Houghton and PEM 1 C, A 3 PEM 1 C (57,499 Sq. Muskego(Hydric) PSS I C, No Ft) PABG Wetlands A Wetland A was a Type 3 shallow cattail marsh with a forested slope to the northeast. The wetland continues to the northwest outside the project area, and stops to the south and southwest when it reaches the project boundary near the edge of Kelly Road. The wetland is surrounded by a thin forested wetland edge along the northern side, but is dominated by cattails. At the time of the delineation, a majority of the wetland was inundated, with the edges of it being saturated at or near the surtace. While delineating the wetland, previous wetland boundary flags were observed, and the current boundary of Wetland A followed the previous delineation boundary closely. 2525 Shadywood Road Page 6 Recommendatians Activities impacting or potentially impacting the wetlands identified are regulated through several levels of government in Minnesota: • Fed2r81: US Army Corps of Engineers: Permit Programs under Section 404 of the Clean Water Act and Section 10 of the Rivers and Harbors Act • Feder8l: USDA NRCS: Wetland Conservation Provisions of the 1996 Farm Bill • State of Minnesota: Minnesota Department of Natural Resources: Public Waters Work Permit Prog ra m • LOCaI: Local Units of Government (LGU) administer the Minnesota Wetland Conservation Act (WCA) of 1991. Please note that grading, excavating, or filling is not allowed until all necessary permits have been obtained. If wetland impacts are proposed, ISG can assist in the proper steps to acquire the appropriate permit or exemption. By initiating the permit process as soon as possible, potential costly delays to the project may be avoided. 2525 Shadywood Road Page 7 Data Sources + Literature Cited Cowardin, L.M., V. Carter, F.C. Golet, and R.T. LA Roe. 1979. Classification of wetlands and deep water habitats of the United States. U.S. Fish and Wildlife Service, FWS/OBS-79/31. Eggers, S.D., and Reed, D.M. 1997. Wetland Plants and Plant Communities of Minnesota and Wisconsin. U.S. Army Corps of Engineers, St. Paul District. 1997. Environmental Laboratory. 1987. Corps of Engineers Wetlands Delineation Manual. Wetlands Research Program Technical Report Y-87-1, US Army Engineers Waterways Experiment Station. Environmental Laboratory. August 2010. Regional Supplement to the Corps of Engineers Wetland Delineation Manual: Midwest Region. ERDC/EL TR-10-16. U.S. Army Corps of Engineers. Lichvar, R.W., D.L. Banks, W.N. Kirchner, and N.C. Melvin. 2016. The Nationa/ Wet/and Plant List: 2016 Wetland Ratings. Phytoneuron 2016-30: 1-17 Minnesota Climatology Working Group. State Climatology Office — DNR Waters, Extension Climatology Office — MES and Academic Climatology — U of Minnesota. http://climate.umn.edu/wetland/ Minnesota Department of Natural Resources Protected Waters Inventory Map, Hennepin County. Shaw, S.P., and C.G. Fredine. 1956. Wetlands of the United States. U.S. Fish and Wildlife Service, Circular 39. 67pp. State of Minnesota Interagency Cooperative Agreement for Implementation of the Federal Wetland Delineation Memorandum of Agreement. Minnesota Wetland Mapping Conventions for 1985 Food Security Act (FSA) as Amended and Section 404 Clean Water Act (CWA), August 1994. United States Army Corps of Engineers- St. Paul District and Minnesota Board of Water&Soil Resources. March 4, 2015. Guidance for Submittal of Delineation Reports to the St. Paul District Army Corps of Engineers and Wetland Conservation Act Local Governmental Units in Minnesota. United States Department of Agriculture. Natural Resources Conservation Service. Climate Analysis for Wetlands. http://www.wcc.nres.usda.aov/ftgref/support/climate/wetlands/ United States Department of Agriculture. Natural Resources Conservation Service. Web Soil Survey. http://websoilsurvey.nres.usda.qov/apq/ United States Fish and Wildlife Service National Wetland Inventory Map. May 2015 Update (April 30, 2015 metadata), Minnesota Department of Natural Resources United States Geological Survey. 7.5 minute, 1:24,000 scale Topographic Quadrangle Map. 2525 Shadywood Road Page 8 APPEN DIX A : Figure 1 . Project Location Figure 2. DNR Public Waters Inventory and National Wetland Inventory Figure 3 . Soil Survey of Hennepin County Figure 4. LiDAR Elevations and Hillshade Figure 5. 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V �.+�' PN:16-19060 Orthophoto(Hennepin Counry,2015) f'IgU(e 6 �� Source(5�: WetlandDelineationQSG,May2016) o zs So lo� Wetland Delineation Map Feee Contours(MN DNR,2011) ,;��n-�oo ree� 2525 Shadywood Road Friday,June 10,2016 Orono, Hennepin County, Minnesota WETLAND DETERMINATION DATA FORM -Midwest Region ProjecUSite 2525 Shadywood Rd City/County: Hennepin Sampling Date: 5-3-16 ApplicanUOwner: Casco Ventures LLC State: MN Sampling Point: SP 1_up Investigator(s): Lucas Mueller 3ection,Township, Range: S20/T117N/R23W Landform(hillslope,terrace,etc.): Hillslope Local relief(concave,convex, none): Slope(%): 0-5 Lat: 44.931786 Long: 93.606424 Datum: NAD 83 Soil Map Unit NameL50A 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 wetland? N Indicators of wetland hydrology present? N f yes,optional wetland site ID: Remarks: (Explain alternative procedures here or in a separate report.) Upland sample point taken in forested area at base of slope before entering wetland A. Above normal precip at time of delineation. Absolute Dominan Indicator pominance Test Worksheet Tree Stratum (Plot size: 30'Rad. ) °/a Cover t Species Staus Number of Dominant Species 1 Fraxinus pennsylvanica 30 Y FACW that are OBL,FACW,or FAC: 3 (A) 2 Rhamnus cathartica 15 Y FAC Total Number of Dominant 3 Species Across all Strata: 4 (B) 4 Percent of Dominant Species 5 that are OBL,FACW,or FAC: 75.00% (A/B) 45 =Total Cover Sa�linq/Shrub straturr (Plot size: 15'Rad. ) Prevalence Index Worksheet 1 Rhamnus cathartica 50 Y FAC Total%Cover of: 2 Zanthoxylum americanum 20 Y FACU OBL species 0 x 1 = 0 3 FACW species 30 x 2= 60 4 FAC species 65 x 3= 195 5 FACU species 20 x 4= 80 70 =Total Cover UPL species 0 x 5= 0 Herb stratum (Plot size: 5'Rad. ) Column totals 115 (A) 335 (B) 1 Prevalence Index=B/A= 2.91 2 3 Hydrophytic Vegetation Indicators: 4 Rapid test for hydrophytic vegetation 5 X Dominance test is>50% 6 X Prevalence index is 53.0* � Morphogical adaptations*(provide 8 supporting data in Remarks or on a 9 separate sheet) 10 Problematic hydrophytic vegetation' 0 =Total Cover (explain) Woodv vine stratum (Plot size: 30'Rad. ) 'Indicators of hydric soil and wetland hydrology must be 1 present,unless disturbed or problematic 2 y rop ytic 0 =Total Cover vegetation present? Y Remarks:(Include photo numbers here or on a separate sheet) Bare ground at time of survey. Minimal vegetation on forest floor. US Amy Corps of Engineers Midwest Region SOIL Sampling Point: SP 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 0-10 10YR 3/1 100 Sandy Loam 10-18 10YR 4/2 97 10YR 4/4 3 D M Sandy Clay Loam 18-24 10YR 4/2 90 10YR 4/6 10 C M Clay Loam *Type: C=Concentration, D=Depletion,RM=Reduced Matrix, MS=Masked Sand Grains. k"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) Iron-Manganese Masses(F12)(LRR K,L,R) Hydrogen Sulfide(A4) Loamy Mucky Mineral(F1) Very Shallow Dark Surface(TF12) Stratified Layers(A5) Loamy Gieyed Matrix(F2) Other(explain in remarks) 2 cm Muck(A10) Depleted Matrix(F3) 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): emarks: HYDROLOGY Wetland Hydrology Indicators: Primarv Indicators(minimum of one is reauired:check all that applvl Secondarv Indicators(minimum of two reauiredl Surface Water(A1) Aquatic Fauna(B13) Surface Soil Cracks(66) High Water Table(A2) True Aquatic Plants(B14) Drainage Pattems(610) Saturation(A3) Hydrogen Sulfide Odor(C1) Dry-Season Water Table(C2) Water Marks(61) Oxidized Rhizospheres on Living Roots Cra�sh Burrows(C8) Sediment Deposits(B2) (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(B5) (C6) FAC-Neutral Test(D5) Inundation Visible on Aerial Imagery(67) Thin Muck SurFace(C7) Sparsely Vegetated Concave Surface(B8) Gauge or Well Data(D9) Water-Stained Leaves(69) Other(Explain in Remarks) Field bservations: Surface water present? Yes No Depth(inches): Water table present? Yes No Depth(inches): Indicators of wetland Saturation present? Yes No Depth(inches): hydrology 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 2525 Shadywood Rd City/County: Hennepin Sampling Date: 5-3-16 ApplicanUOwner: Casco Ventures LLC State: MN Sampling Point: SP 2-wet Investigator(s): Lucas Mueller 3ection,Township, Range: S20/T117N/R23W Landform(hillslope,terrace,etc.): Depression Local relief(concave,convex, none): Slope(%): 0-5 Lat: 44.931752 Long: 93.60651 Datum: NAD 83 Soil Map Unit NameL50A VWI Classification: PEM1C 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 wetland? Y Indicators of wetland hydrology present? Y f yes,optional wetland site ID: Remarks:(Explain alternative procedures here or in a separate report.) Taken on edge of Type 3 wetland. Edge of wetland is semi-forested.Above normal precip at time of delineation. VEGETATION -- Use scientific names of plants. Absolute Dominan Indicator pominance Test Worksheet Tree Stratum (Plot size: 30'Rad. ) %Cover t Species Staus Number of Dominant Species 1 Fraxinus pennsylvanica 30 Y FACW that are OBL,FACW,or FAC: 5 (A) 2 Rhamnus cathartica 5 N FAC Total Number of Dominant 3 Species Across all Strata: 5 (B) 4 Percent of Dominant Species 5 that are OBL,FACW,or FAC: 100.00% (A/B) 35 =Total Cover Saolinq/Shrub straturr (Plot size: 15'Rad. ) Prevalence Index Worksheet 1 Fraxinus pennsylvanica 10 Y FACW Total%Cover of: 2 Rhamnus cathartica 10 Y FAC OBL species 0 x 1 = 0 3 FACW species 90 x 2= 180 4 FAC species 15 x 3= 45 5 FACU species 0 x 4= 0 20 =Total Cover UPL species 0 x 5= 0 Herb stratum (Plot size: 5'Rad. ) Column totals 105 (A) 225 (B) 1 Phalaris arundinacea 40 Y FACW Prevalence Index=B/A= 2.14 2 Urtica dioica 10 Y FACW 3 Hydrophytic Vegetation Indicators: 4 Rapid test for hydrophytic vegetation 5 X Dominance test is>50% 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* 50 =Total Cover (explain) Woodv vine stratum (Plot size: 30'Rad. ) `Indicators of hydric soil and wetland hydrology must be � present,unless disturbed or problematic 2 y rop ytic 0 =Total Cover vegetation present? Y Remarks:(Include photo numbers here or on a separate sheet) 40% bare soil at sample point location. US Amy Corps of Engineers Midwest Region SOIL Sampling Point: SP 2-wet Profile Description: (Describe to the depth needed to document the indicator or confrm the absence of indicators.) Depth Matrix Redox Features (Inches) Color(moist) % Color(moist) % Type' Loc*" Texture Remarks 0-10 10YR 3/1 100 Mucky Mineral 10-24 10YR 4/2 80 10YR 4/6 20 D M Clay Loam Depletions Observed at 10" *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) Iron-Manganese Masses(F12)(LRR K,L,R) Hydrogen Sulfide(A4) X Loamy Mucky Mineral(F1) Very Shallow Dark Surface(TF12) Stratified Layers(A5) Loamy Gleyed Matrix(F2) Other(explain in remarks) 2 cm Muck(A10) Depleted Matrix(F3) 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? Y Depth(inches): emar s: HYDROLOGY Wetland Hydrology Indicators: Primarv Indicators(minimum of one is reauired:check all that applv) Secondarv Indicators(minimum of two reauired) Surface Water(A1) Aquatic Fauna(613) Surface Soil Cracks(66) X High Water Table(A2) True Aquatic Plants(B14) Drainage Pattems(B10) X Saturation(A3) Hydrogen Sulfide Odor(C1) Dry-Season Water Table(C2) Water Marks(61) Oxidized Rhizospheres on Living Roots Cra�sh Burrows(C8) Sediment Deposits(B2) (C3) �Saturation Visible 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 X Geomorphic Position(D2) Iron Deposits(65) (C6) FAC-Neutral Test(D5) Inundation Visible on Aerial Imagery(67) Thin Muck Surface(C7) Sparsely Vegetated Concave Surface(B8) Gauge or Well Data(D9) Water-Stained Leaves(69) Other(Explain in Remarks) Field bservations: Surface water present? Yes No Depth(inches): Water table present? Yes X No Depth(inches): 2 Indicators of wetland Saturation present? Yes X No Depth(inches): 1 hydrology 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 2525 Shadywood Rd City/County: Hennepin Sampling Date: 5-3-16 ApplicanUOwner: Casco Ventures LLC State: MN Sampiing Point: SP 3-wet Investigator(s): Lucas Mueller 3ection,Township, Range: S20lf117N/R23W Landform(hillslope,terrace,etc.): Depression Local relief(concave,convex,none): Slope(%): 0-5 Lat: 44.93147 Long: 93.606029 Datum: NAD 83 Soil Map Unit NameL50A VWI Classification: PEM1C Are climatic/hydrologic conditions of the site typicai 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 wetland? Y Indicators of wetland hydrology present? Y F yes,optional wetland site ID: Remarks:(Explain alternative procedures here or in a separate report.) Taken on edge of Type 3 wetland. Edge of wetland is semi-forested. Above normal precip leading up to delineation. VEGETATION --Use scientific names of plants. Absolute Dominan Indicator pominance Test Worksheet Tree Stratum (Plot size: 30'Rad. ) °/a Cover t Species Staus Number of Dominant Species 1 Acer negundo 30 Y FAC that are OBL,FACW,or FAC: 5 (A) 2 Rhamnus cathartica 5 N FAC Total Number of Dominant 3 Species Across all Strata: 6 (B) 4 Percent of Dominant Species 5 that are OBL,FACW,or FAC: 83.33% (A/B) 35 =Totat Cover Saplinq/Shrub straturr (Plot size: 15'Rad. ) Prevalence Index Worksheet 1 Fraxinus pennsylvanica 10 Y FACW Total%Cover of: 2 Rhamnus cathartica 10 Y FAC OBL species 0 x 1 = 0 3 Acer negundo 10 Y FAC FACW species 45 x 2= 90 4 FAC species 55 x 3= 165 5 FACU species 20 x 4= 80 30 =Total Cover UPL species 0 x 5= 0 Herb stratum (Plot size: 5'Rad. ) Column totals 120 (A) 335 (B) 1 Phalaris arundinacea 30 Y FACW Prevalence Index=B/A= 2.79 2 Urtica dioica 5 N FACW 3 Chenopodium album 5 N FACU Hydrophytic Vegetation Indicators: 4 Rapid test for hydrophytic vegetation 5 X Dominance test is>50% 6 X Prevalence index is<_3.0" � Morphogical adaptations'(provide $ supporting data in Remarks or on a 9 separate sheet) 10 Problematic hydrophytic vegetation" 40 =Total Cover (explain) Woodv vine stratum (Plot size: 30'Rad. ) *Indicators of hydric soil and weUand hydrology must be 1 Vitis aestivalis 15 Y FACU present,unless disturbed or problematic 2 y rop ytic 15 =Total Cover vegetation present? Y Remarks:(Include photo numbers here or on a separate sheet) 40% bare soil at sample point location. US Amy Corps of Engineers Midwest Region SOIL Sampling Point: SP 3-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 0-6 10YR 3/1 100 Mucky Mineral 6-16 10YR 4/1 80 10YR 4/6 20 D M Clay Loam Depletions Observed at 10" 16-24 10YR 5/3 95 10YR 4/6 5 C 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 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) Iron-Manganese Masses(F12)(LRR K,L,R) Hydrogen Sulfide(A4) X Loamy Mucky Mineral(F1) Very Shallow Dark Surface(TF12) Stratified Layers(A5) Loamy Gleyed Matrix(F2) Other(explain in remarks) 2 cm Muck(A10) Depleted Matrix(F3) 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? Y Depth(inches): emarks: HYDROLOGY Wetland Hydrology Indicators: Primarv Indicators(minimum of one is reauired:check all that aaplvl Secondarv Indicators(minimum of two reauired) Surface Water(A1) Aquatic Fauna(B13) Surface Soil Cracks(66) X High Water Table(A2) True Aquatic Plants(614) Drainage Pattems(610) X Saturation(A3) Hydrogen Sulfide Odor(C1) Dry-Season Water Table(C2) Water Marks(B1) Oxidized Rhizospheres on Living Roots Cra�sh Burrows(C8) Sediment Deposits(62) (C3) �Saturation�sible 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) FAC-Neutral Test(D5) Inundation Visible on Aerial Imagery(67) Thin Muck SurFace(C7) Sparsely Vegetated Concave Surface(B8) Gauge or Well Data(D9) Water-Stained Leaves(B9) Other(Explain in Remarks) Field bservations: Surface water present? Yes No Depth(inches): Water table present? Yes X No Depth(inches): 3 Indicators of wetland Saturation present? Yes X No Depth(inches): 2 hydrology 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 2525 Shadywood Rd City/County: Hennepin Sampling Date: 5-3-16 ApplicanUOwner: Casco Ventures LLC State: MN Sampling Point: SP 4_up Investigator(s): Lucas Mueller 3ection,Township, Range: S20/T117N/R23W Landform(hillslope,terrace,etc.): Hillslope Local relief(concave,convex,none): Slope(%): 0-5 Lat: 44.931462 Long: 93.605934 Datum: NAD 83 Soil Map Unit NameL50A 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 wetland? N Indicators of wetland hydrology present? N f yes,optional wetland site ID: Remarks:(Explain alternative procedures here or in a separate report.) Upland sample point taken in forested area at base of slope before entering wetland A.Above normal precip leading up to delineation. VEGETATION -- Use scientific names of plants. Absolute Dominan Indicator pominance Test Worksheet Tree Stratum (Plot size: 30'Rad. ) %Cover t Species Staus Number of Dominant Species 1 Acer negundo 30 Y FAC that are OBL,FACW,or FAC: 4 (A) 2 Rhamnus catharfica 15 Y FAC Total Number of Oominant 3 Species Across all Strata: 4 (B) 4 Percent of Dominant Species 5 that are OBL,FACW,or FAC: 100.00% (A/B) 45 =Total Cover Sa�lina/Shrub straturr (Plot size: 15'Rad. ) Prevalence Index Worksheet 1 Rhamnus cathartica 50 Y FAC Total%Cover of: 2 Zanthoxylum americanum 5 N FACU OBL species 0 x 1 = 0 3 FACW species 0 x 2= 0 4 FAC species 135 x 3= 405 5 FACU species 25 x 4= 100 55 =Total Cover UPL species 0 x 5= 0 Herb stratum (Plot size: 5'Rad. ) Column totals 160 (A) 505 (B) 1 Alliaria petiolata 40 Y FAC Prevalence Index=B/A= 3.16 2 Bromus inermis 10 N FACU 3 Vicia sativa 10 N FACU Hydrophytic Vegetation Indicators: 4 Rapid test for hydrophytic vegetation 5 X Dominance test is>50% 6 Prevalence index is<_3.0* � Morphogical adaptations*(provide $ supporting data in Remarks or on a 9 separate sheet) 10 Problematic hydrophytic vegetation* 60 =Total Cover (explain) Woodv vine stratum (Plot size: 30'Rad. ) "Indicators of hydric soil and wetland hydrology must be 1 present,unless disturbed or problematic 2 y rop ytic 0 =Total Cover vegetation present? Y Remarks:(Include photo numbers here or on a separate sheet) Some bare soil on forest floor at time of survey US Amy Corps of Engineers Midwest Region SOIL Sampling Point: SP 4_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 0-10 10YR 3/1 100 Sandy Loam 10-14 10YR 4/2 100 Sandy Clay Loam 14-24 10YR 5/2 90 10YR 4/6 10 C 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 Hydric Soils: Histisof(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) Iron-Manganese Masses(F12)(LRR K, L,R) Hydrogen Sulfide(A4) Loamy Mucky Mineral(F1) Very Shallow Dark Surface(TF12) Stratified Layers(A5) Loamy Gleyed Matrix(F2) Other(explain in remarks) 2 cm Muck(A10) Depleted Matrix(F3) 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): emar s: HYDROLOGY Wetland Hydrology Indicators: Primarv Indicators(minimum of one is reauired:check all that applv) Secondarv Indicators(minimum of two repuired) Surface Water(A1) Aquatic Fauna(B13) SurFace Soil Cracks(66) High Water Table(A2) True Aquatic Plants(B14) Drainage Pattems(610) Saturation(A3) Hydrogen Sulfide Odor(C1) Dry-Season Water Table(C2) Water Marks(61) Oxidized Rhizospheres on Living Roots Cra�sh Burrows(CS) 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 Ti�led 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(68) Gauge or Well Data(D9) Water-Stained Leaves(B9) Other(Explain in Remarks) Fie d Observat�ons: Surface water present? Yes No Depth(inches): Water table present? Yes No Depth(inches): Indicators of wetland Saturation present? Yes No Depth(inches): hydrology 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 1 � � , � ' ' • ' � ' � . i � . . � • • • � 2525, 2535, and 2545 Shadywood Road Appendix C 2525, 2535, 2545 Shadwvood Road Wetland Investigation Precipitation Worksheet for Wetland Delineation Date: 5/3/2016 Location: Orono, Hennepin County � �_ , �: 1 st Month Prior April' 2.14 2.52 2.90 3.44 Wet 3 3 9 2nd Month Prior March' 1.07 1.55 2.03 1.09 Normal 2 2 4 3rd Month Prior February' 0.42 0.66 0.87 0.90 Wet 3 1 3 Precipitation Data Source: httpJ/climate.umn.edu/gridded data/precip/vvetland/wetland.asp SUM= 16 'Preliminary Climate Dafa irom Twin Cities station (http✓/www.dnr.state.mn.us/climate/historical/Icd.html?loc=msp) Condition Value: Dry = 1 Normal = 2 Wet = 3 - Note- If sum is: 6 - 9 = Dry 10 - 14 = Normal 15 - 18 = Wet . ,;: ,� �� _ , ,`-0 ar `� 1.'� .� ��,. y s�";` �j •;•� i � 'q� �y'' '' 4• . ��°� +`' '„ . 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' ..�H �-. �R rs.�. �S +S ►�~ .1�t��i�iw � 4�yJ �('k'yi` �p/� ',7i 31 ' �� ,�,� .� -y;�'ti�� �: y�dj f��� �: ,��t,`y, I'4� .�4� :L�'�.'�',�r."i�7i'"1-�..1't .'.•*:Y_ .���i:'i�s '�i����i�..�`1 Photo 1 taken on north edge of project area facing northeast, showing shrub/scrub upland area "� �# � �';�`�,. �y� :� � � ��� � ��'a� � � � �5. ,,k.•.`�4�- ' R I' j ;at�� Y�A F y � �i � i� � /(y'y' y�'� '{' I`• 1 ' f � I � '�;M1 .f`. , . �.,'1 l'�. , � �� � � �� �; 4,.1���, . 1 ; � � i a. r � + 'P�h � '�r��i'! { ����� �����1h, � ��l �, . I• � � 1 �� J :� �JR'���j.. r , � V * `�.. . �IVLv � lrJ�'\CII IICai IIVI��iIVVCS� I.UIIICi '.�I YYClIC71lU hl iq�.IIIIJ, JUULIICCI��. 2525 Shadywood koad, Orono, MN Appendix C - 1 r�!. � � r �,r. 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'� :V", , 4 � . � � Y..{� , ��.� ���� .��,. �:rl ; - � � �:� r���tc � ��K_��� �,����y nortl� tdye ot wetland facing sout�� showing Wetland A. � ��;�: r� ' � ��1� ,���� �. i'' ' ,�r /! ,,'y � . -; �'. `,t �, r� ti r� � 1�� 'i.,,f� �L„• � ..� .l�[,t � �,`4. ��.(A� ''k��� `y�(�e f i t.✓. � �J aY x ( v�i�� ` .,� .� s�r/!' +�' �� � � � � ��� � .�C:, � � t • i . � � •r 4 �r.' ��i �t ,r , �" � � ' ,� � f ;'�,i.. �t' �., ;-* 'Y`1 �, T��� .�{ ;.r� ' � r" +�i 'n, '`,. ►? - r n. i �r��e�� ��! � ;, � r✓- .- .�''�,.� � C�r� �. 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Project Name and/or Number: 2525.2535,2545 5hadvwood Road,Orono,MN 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(nformation must also be provided. Applicant/Landowner Name: Casco Ventures LLC(Todd Holmers) Mailing Address: 16192 Highway 7,Excelsior,MN 55331 Phone: (612)991-9777 E-maii Address: toddholmers@gmail.com Authorized Contact(do not complete tf same as above): Mailing Address: Phone: E-mail Address: Agent Name: Lucas Mueller,ISG Matling Address: 79001nternational Drive,5uite 550,Minneapolis,MN 55425 Phone: (952)429-0699 E-matl Address: lucas.mueller@is-sra.com PART TWO: Site location Information County: Hennepin City/Township: Orono Parcel ID and/or Address: 2525,2535,and 2545 5hadywood Road,Orono,MN(PID No.2011723110030,2011723110029, 2011723110028) Legal Description(Section,Township,Range): Section 20,T117N,R23W Lat/Long(decimal degrees): 44.9314, -93.6063 Attach a map showing the location of the sRe in relation to local streets,roads,highways. 5ee attached location map Approximate size of site(acres)or if a Iinear project,length(feet): 3.66 acres If you know that your proposai 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/reaulatorv/ReaulatorvDocs/enaform 4345 2012oct odf PART THREE: General Project/Site Information If this application is related to a delineation approval,exemption determination,jurisdictional determination,or other correspondence submitted prlor to this application then describe that here and provide the Corps of Englneers 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 lncluding a description of all project elements that effect aquatic resources(wedand,lake,tributary,etc.)and must also include plans and cross section or profile drawings showing the location,character,and dimensions of all proposed actfvities and aquatic resource impacts. Wetland Delineation � Project Name and/or Number: 2525,2535,2545 Shadvwood Road,Orono,MN PART FOUR: Aquatic Resource Impact15ummary 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 wlth a reference number or letter and identify the impacts in the following table. Type of Impact Duratton of County,Major Aquatic Existing Plant Aquatic Resource (fill,excavate, Impact Overall Size of Watershed#, Resource Type Community ID(as noted on draln,or Permanent(P) Size of ImpactZ Aquatic and Bank overhead view) �Wetland,lake, remove or Temporary Resource 3 Type(s)�n Service Area# tributary etc.) impact Area4 vegetation) ('�1 of Impact Area 11f 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 woutd be entered`T(220)". =Impacts 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 flrst 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 square feet). 3This is generally only applicable if you are applying for a de minimis exemptton under MN Rules 8420.0420 Subp.8,otherwlse enter"N/A". °Use Wetland P/ants and Plant Community Types ojMlnnesofa and Wisconsln 3�Ed.as modified in MN Rules 8420.0405 Subp.2. SRefer to Major Watershed and Bank Serv(ce 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: 1 The term"ImpacY'as used in this joint applicatlon form Is a generic term used for disclosure purposes to identify activities that may require approval from one or more regulatory agencies. For purposes ot this form it is not meant to fndicate whether or not those activities may require mitigation/replacement. Project Name and/or Number: 2525,2535,2545 Shadvwood Road.Orono.MN 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 �Dellneatlon Concurrence. Concurrence with a delineation is a written noti�cation from the Corps and a decision from the LGU concurring,not concurring,or commenting on the boundaries of the aquatic resources dellneated on the properry.Delineation concurrences are generally valid for five years unless slte conditions change.Under thls 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.). ❑PreliminaryJurisdictional Determination.A preliminaryjurisdictional 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 advfsory in nature and may not be appealed. ❑Approved Jurisdictional Determinatlon.An approved jurisdictlonal determination(AJD)is an official Corps determination that jurisdictional waters of the Untted States are either present or absent on the property.AIDs can generally be relied upon by the affected parry for five years.An AlD may be appeated 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 fnr Submitting Wetland Delfneafions in Minnesota(2013). http://www.mvp.usace.armv.mil/Missions/Re�ulatorv/DelineationlDGuidance.aspx Project Name and/or Number: 2525,2535,2545 Shadvwood Road,Orono, MN 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 atcurate. I further attest that I possess the authority to undertake the work described herein. c Signat . ^'� ---. Date: 06/02/16 I hereby authorize ISG 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. WATER RESOURCE PERNIIT aPPLiCATI01�' FORM Use this fvrm to notifplapply to the �linnehaha Creek Watershed Uistrict(MCWD)ofa prop�sed project or work which may fall within their jurisdiction. Fill out this form complctcly and sub►nit with your sitc rlan,maps,ctc. to thc MCWU at: 15320 Minnctonka Blvd.Minnetonka,MN 55345. Keep a copy for yom•records. � YOU MUST OBTAIN ALL REQUIRED AUTHORIZATIONS BEFORE BEGINNING WORK. 1. Nan1e of each property owner: l � �/ ',c� �- /i � �� E � � Mailing Address: /S C �� f� 1 ti�-� C' /E +'� k City: C'__ l+� ����, State: /l�i�_.Zip: �� s - i Email Address: y��Q��r k, � �i�� 1 _, �e�:� Phone���l_31 F'�-1 =�� � Fax:i5��- 23 3 - 2 �i z_ 2. Property Owner Representative Infocmation (not required) (licensed contractor, architect, engineer, etc...) Business Name: �s� Representative Name: T�a��s Fr�sted BUSII]e5S AC1CIreSs: 7900 International Drive,Suite 550 Clty: Bloomington State: MN Zjp; 55425 E(IIaII A[ICII'eSS: travis.fristed@is-grp.com Phone: ss2-a2s-osss Fax: 3. Project Address: 25z5,2535,and 2545 Shadywood Road CICy: Orono State: MN Zjp: 55331 (,�tr SeCitOtt(S�: NE Section(s): 20 Township(s): ��� Range(s): 23w Lot: Block: Subdivision: PID: 2o>>ns��ooso.2011723110029, 2011723110028 4. Size of project parcel (square feet or acres): 3.6�ac�es Area of disturbance (square feet): "o�aPPncabie Volume of excavation/fill (cubie yards): No�a�pi�canie Area of existing impervious surface: Nor a,PPr�abie �rea of proposed impervious surface: Noi appitcabie Length of shoreline affected (feet): N�A Waterbody(& bay if applicable): Not apPr�abie 5. Type of pennit being applied for(Check all that apply): ❑ EROSION CONTROL ❑ WATERBODY CROSSINGS/STRUCTURES ❑ FLOODPLAIN ALTERATiON ❑ Sl'ORMWATER MANAGEMENT �( WETLAND PROTECTION ❑ APPROPR[ATIONS � DREDGING ❑ ILLICIT DISCHARGE ❑ SHORELTNE/STREAMBANK STABILIZATION 6. Project purpose (Check all that apply): ❑ SINGLE FAMILY HOME O MULTI FAMILY RES(DENTIAL(apartments) ❑ ROAD CONSTRUCTION ❑ COMMERCIAL or INSTITUTIONAL O UT1LI1'IES ❑ SUBDIVISInNS (include number of lots) ❑ DREDGING ❑ Lt1NDSCAPING(pools, berms,etc.) ❑ SHORELINE/STREAMBANK STABILIZATION � OTI�ER(DESCRtBE): Land Survey 7. NPDES/SDS General Stormwater Permit Number(if applicable): Not APPn�abte 8. Waterbody receiving runoff from site: u�k�own 9. Project Timeline: Starl Dale: To Be�eterm+��d Completion Date: Penni[s have been applied for: City County MN Pollution Control Agency DNR COE Permits have been received: Ciry County MN Pollution Control Agency DNR COE By signing bclow,1 hcrcby rcqucst a permit to authorizc thc activitics dcscribcd hcrcin. [ccrtify that 1 am familiar with MCWD Rules and that thc proposed activity will be conducced in compliance wid�tl�ese Rules. I am familiar with the information contained in this application and, to the best of my knowledgc and bclicf,all infonnation is true,complete and accurate. 1 understand that proceedinb with work before all required authorizations are obtained may be subject to federal,state and/or local administrative,civil and/or criminal penalties. � - , ��� ��'�� 7/7 /iG 'gnature of ch Prope Owner Datc