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wetland delineation/2015
930 Partenwood Road Orono, Minnesota Wetland Delineation Report Prepared for Kirk& Pam Moore by Kjolhaug Environmental Services Company, Inc. (KES Project No. 2015-095) August 18, 2015 WETLAND DELINEATION SUMMARY • The 1.2 acre 930 Partenwood Road Properiy was inspected on July 7, 2015 for the presence and extent of wetland. • The NWI-map showed one PEM1C/L2ABH wetland/waterbody within the property. • The soil survey showed Tadkee as the hydric soil type present within the review area. • The DNR Public Waters map showed DNR Public Water 27-133P (Lake Minnetonka) within 1000' of the property. • One Type 3 (PEM 1 C) shallow marsh was delineated within the review area. 1 930 Partenwood Road Orono, Minnesota Wetland Delineation Report I. INTRODUCTION The approximately 1.2 acre Partenwood Road Property was inspected on July 7, 2015 for the presence and extent of wetland. The property was located in Section 8, Township 117N, Range 23W, Orono, Hennepin County, Minnesota. Generally the site location was west of Lake Minnetonka and east of Tonkawa and Partenwood Road (Figure 1). The site limits corresponded to Hennepin County PID 0811723210007. The site was dominated by manicured lawn with scattered hardwood trees. A single-family home was located near the northwestern portion of the site. Adjacent land use was primarily single-family homes,hardwood forest, and Lake Minnetonka. The site sloped from west to east with elevations ranging from 970' at the west end to 930' at the lakeshore. One depressional wetland was identified and delineated along the eastern parcel boundary(adjacent to Lake Minnetonka) (Figure 2). II. METHODS Wetlands were identified using Routine Determination methodology described in the Corps of Engineers Wetlands Delineation Manual (Waterways Experiment Station, 1987) and Regional Supplement to the Corps of Engineers Wetland Delineation Manual: Midwest Region(Version 2.0) as required by Section 404 of the Clean Water Act and the Minnesota Wetland Conservation Act. Wetland boundaries were identified as the upper-most extent of wetlands, which met criteria for hydric soils, hydrophytic vegetation, and wetland hydrology. Wetland-upland boundaries were marked with pin flags and were located by a Trimble Juno GPS unit. Soils, vegetation, and hydrology were documented at representative locations along the wetland- upland boundary. Plant species dominance was estimated based on the percent aerial or basal coverage visually estimated within a 30-foot radius for trees and vines, 15-foot radius for the shrub layer, and a 5-foot radius for the herbaceous layer within the community type being sampled. Soils were characterized to a minimum depth of 18-24 inches (unless otherwise noted) utilizing Munsell Soil Color Charts and standard soil texturing methodology. Hydric soil indicators used in reporting are from the NTCHS Field Indicators of Hydric Soils in the United States (USDA Natural Resources Conservation Service Version 7, 2010)which are commonly found in the Midwest. 2 Plants were identified using standard regional plant keys. Taxonomy and indicator status of plant species was taken from the 2014 National Wetland Plant List (Lichvar, R.W. and Kartesz, J.T. 2009. North American Digital Flora:National Wetland Plant List, version 2.4.0 (https://wetland�lants.usace.army.mil). U.S. Army Corps of Engineers, Engineer Research and Development Center, Cold Regions Research and Engineering Laboratory, Hanover,NH, and BONAP, Chapel Hill, NC.) III. RESULTS Review of NWI. Soils, and DNR Information The National Wetland Inventory Map (NWI) (Excelsior Quadrangle, MN DNR 2013) showed one PEM 1 C/L2ABH wetland/waterbody within the property(Figure 3). The Soil Survey of Hennepin County,Minnesota (http://soils.usda.gov/survey/geography/ssurgo/) showed Tadkee as the hydric soil type present within the review area. A soils map indicating the soil types present within the parcel is included on Figure 4 The DNR Public Waters Map,Hennepin County(http://deli.dnr.state.mn.usn showed DNR Public Water 27-133P (Lake Minnetonka)within 1000' of the properly (Figure 5). The National Hydrography Dataset Map (USGS) showed Lake Minnetonka bordering the property to the east (Figure 6). Wetland Determinations and Delineations Potential wetlands were evaluated in greater detail during field observations on July 7, 2015. One(1) wetland was identified within the subject parcel (Figure 2). Corresponding data forms are included in Appendix A. The following description of the wetland and its adjacent upland reflects conditions observed at the time of the field visit. At that time precipitation totals were greater than typical based on available 30-day rolling precipitation data and normal based on the three-month antecedent conditions (April, May, June) (Appendia�B). Wetland 1 was a Type 3 (PEM 1 C) shallow marsh. The wetland was dominated by a fringe of reed canary grass,pinkweed, and jewelweed with cattail present along the water's edge of Lake Minnetonka. Saturation was observed at the surface of the sample point location with free water observed 6"below the soil surface. Adjacent upland at the sample location was dominated by sugar maple,basswood, and ironwood trees with a sparse herbaceous layer consisting of early meadow rue and common buckthorn. The delineated boundary followed an abrupt change in topography and was placed along the transition zone from wetland to upland plant communities, where hydrology indicators were no longer present, and the transition from hydric to non-hydric soils. Wetland 1 was indicated on the NWI map as a PEM 1 C/L2ABH wetland/waterbody and was located in an area of mapped Tadkee(hydric) on the soil survey. 3 Other Areas The NWI map indicates no additional wetland on the property, non-hydric soil is mapped throughout the majority of the site. No other areas with wetland vegetation or hydrology were observed on the site. 4 IV. CERTIFICATION OF DELINEATION The procedures utilized in the described delineation are based on the COE 1987 Wetland Delineation Manual as required by Section 404 of the Clean Water Act and the Minnesota Wetland Conservation Act. Both the delineation and report were conducted in compliance with regulatory standards in place at the time the work was completed. All site boundaries indicated on figures within this report are approximate and do not constitute an official survey product. Delineation Completed by: Ben Carlson, Wetland Specialist Certified Wetland Delineator No. 1125 � Report reviewed by: Date: August 18, 2015 Mark Kjolhaug, Professional Wetland Scientist No. 000845 5 930 Partenwood Road Wetland Delineation Report Figures: • Figure 1 — Site Location Map • Figure 2—Existing Conditions Map • Figure 3 —NWI Map • Figure 4—Soil Survey Map • Figure 5 —DNR Protected Waters Map • Figure 6—National Hydrography Dataset Map ' " � �� � ��' -�� �`� ..��� � �� � .���'��� � � m'S , � ., �„, �,,� ��y,�����^���t,m'��,a. �� t q r '�s"s,�,st����'�:�� �' � �� �, �r �r �`�i `�r x' ` �F '� � a�- a a, .� �'� �§^� �'bi �k � � „ � '�`z� � t" �s�� s� � ' t ,�.� ,� � s��;' �. „,��.a �'a«: �, � ��. . 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Figure 3 - National Wetiand lnventory Map (2013 MN llNl�) N 930 Partenwood Rd (KES 2015-095) �' � 0 100 200 Orono,Minnesota � .._ � Feet Note:Boundaries indicated T Tu� on this figure are approximate KJOL1111UG ENVIRONMENTAL SERVICES COMPANY and do not constitute an "�"�-�'" official survey product. �1v Map unit ~ �;'�,`4. L35A Lerdal Map unit name Rating � �• symbol � ;�,.� � � ;� L40B Angus-Kilkenny complex, 2to 6 percent Predominantly , y� ► " slopes Non-Hydric �; �" �� Lester-Kilkenny complex, 6to 12 percent Predominantly , �§ . s ; �.,, L41C2 . slopes, eroded Non-Hydric :����,�* � � �j_, �' "' . �,�.���� ` �. , L41E Lester-Kilkenny complex, 18to 25 Predominantly � ;,�: ;;� .� � percent slopes Non-Hydric + R ' � � � ,�MA � � r�'� r",� ."`-`' `s�. Tadkee-Tadkee,depressional, complex, Predominantly � , 6 , L64A ',* � �;��. (1tc � � ., i..,.,r,< H�i�lri( �;.��'��."#+,� ��i �' �.. ��� p.tia�. �� � � � P'.' _'Ak` .. 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Y (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 remarics.) Hydrophytic vegetation present? N 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.) Precipitation above typical based on 30-day rolling total, 3-months prior were normal. 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 Acer saccharum 60 Y FACU that are OBL,FACW,or FAC: 1 (A) 2 Tilia americana 30 Y FACU Total Number of Dominant 3 Ostrya virginiana 5 N FACU Species Across all Strata: 4 (B) 4 Percent of Dominant Species 5 that are OBL,FACW,or FAC: 25.00% (A/B) 95 =Total Cover Saqlinct/Shrub straturr (Plot size: 15' ) Prevalence Index Worksheet 1 Total%Cover of: 2 OBL species 0 x 1 = 0 3 FACW species 0 x 2= 0 4 FAC species 5 x 3= 15 5 FACU species 100 x 4= 400 0 =Total Cover UPL species 0 x 5= 0 Herb stratum (Plot size: 5' ) Column totals 105 (A) 415 (B) 1 Rhamnus cathartica 5 Y FAC Prevalence Index=B/A= 3.95 2 Thalictrum dioicum 5 Y FACU 3 Hydrophytic Vegetation Indicators: 4 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 9 separate sheet) 10 Problematic hydrophytic vegetation* 10 =Total Cover (explain) Woodv vine stratum (Plot size: 30' ) •Indicators of hydric soil and wetland hydrology must be 1 present,unless disturbed or problematic 2 y rop ytic 0 =Total Cover vegetation present? N Remarks:(Include photo numbers here or on a separate sheet) US Amy Corps of Engineers Midwest Region SOIL Sampling Point: 1-1 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 3/2 100 Clay loam 10-18 10YR 4/3 100 Clay loam *Type: C=Concentration, D=Depletion, RM=Reduced Matrix, MS=Masked Sand Grains. "Location: PL= Pore Lining, M=Matrix Hydric Soil lndicators: 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 problematic Restrictive Layer(if observed): Type: Hydric soil present? N Depth(inches): Remarks: 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(613) 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(B1) Oxidized Rhizospheres on Living Roots Cra�sh 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(64) 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(BS) Gauge or Well Data(D9) Water-Stained Leaves(B9) Other(Explain in Remarks) Field Observations: Surface water present? Yes No X Depth(inches): Water table present? Yes No X Depth(inches): Indicators of wetland Saturation present? Yes No X Depth(inches): hydrology present? N (includes capillary fringe) Describe recorded data(stream gauge, monitoring well, aerial photos,previous inspections), if available: emarks: US Army Corps of Engineers Midwest Region WETLAND DETERMINATION DATA FORM -Midwest Region Project/Site 930 Partenwood Road City/County: Orono/Hennepin Sampling Date: 7/7/2015 ApplicanUOwner: Kirk&Pam Moore State: MN Sampling Point: 1-1 Wet Investigator(s): BPC(WDC#1125) 3ection,Township, Range: S 8,T117N, R23W Landform(hillslope,terrace,etc.): Basin Local relief(concave,convex, none): Concave Slope(%): 1 Lat: Long: Datum: Soil Map Unit NameTadkee(Hydric) VWI Classification: PEM1C Are climatic/hydrologic conditions of the site typical for this time of the year? Y (If no,explain in remarks) Are vegetation ,soil ,or hydrology significantly disturbed? Are"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.) Precipitation above typical based on 30-day rolling total, 3-months prior were normal. 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: 4 (A) 2 Total Number of Dominant 3 Species Across all Strata: 4 (B) 4 Percent of Dominant Species 5 that are OBL,FACW,or FAC: 100.00% (A/B) 0 =Total Cover Saqlina/Shrub straturr (Plot size: 15' ) Prevalence Index Worksheet 1 Rhamnus cathartica 5 Y FAC Total%Cover of: 2 OBL species 5 x 1 = 5 3 FACW species 40 x 2= 80 4 FAC species 5 x 3= 15 5 FACU species 0 x 4= 0 5 =Total Cover UPL species 0 x 5= 0 Herb stratum (Plot size: 5' ) Column totals 50 (A) 100 (B) 1 Impatiens capensis 20 Y FACW Prevalence Index=B/A= 2.00 2 Phalaris arundinacea 10 Y FACW 3 Persicaria pensylvanica 10 Y FACW Hydrophytic Vegetation Indicators: 4 Cicuta maculata 5 N OBL 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' 45 =Total Cover (explain) Woodv vine stratum (PIOt SiZB: 30' ) *Indicators of hydric soil and wetland hydrology must be 1 present,unless disturbed or problematic 2 y rop yt�c 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: 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 0-6 N 2.5/0 100 Oa(Sapric) 6-18 10YR 5/1 90 5GY 5/1 10 RM M Mucky Mineral *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 Daric 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 problematic Restrictive Layer('rf observed): Type: Hydric soil present? Y Depth(inches): Remarks: 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(B6) X High Water Table(A2) True Aquatic Plants(B14) Drainage Patterns(610) 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(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(65) (C6) X FAC-Neutral Test(D5) Inundation Visible on Aerial Imagery(67) Thin Muck Surface(C7) X Sparsely Vegetated Concave Surface(68) Gauge or Well Data(D9) Water-Stained Leaves(B9) Other(Explain in Remarks) Field bservations: Surface water present? Yes No X Depth(inches): Water table present? Yes X No Depth(inches): 6 Indicators of wetland Saturation present? Yes X No Depth(inches): 0 hydrology present? Y (includes capillary fringe) Describe recorded data(stream gauge,monitoring well,aeriaf photos, previous inspections), if available: Remarks: US Army Corps of Engineers Midwest Region 930 Partenwood Road Wetland Delineation Report Appendix B: Precipitation Data g ____._______._...------------------- .�---------------------------------------- - - ----� y 7 3rd Prior 30 Days 2nd Prior 30 Days 1 st Prior 30 Days a� � s � c, i � Site Visit 7/7/15 � c 6 0 � ca � .Q 'v 5 a� � � � O 4 � >+ • s . - . . - � c � 3 � � � � T >+ 2 •� 30 - day rolling total � T 1 - T T T - I T �, '' T 0 I I � 4/7/15 4/22/15 5/7/15 5/22/15 6/6/15 6/21/15 7/6/15 o monthly precip — daily precip 30d rolling total