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HomeMy WebLinkAbout2010-09-23 Wetland Delineation Report AutoZone — Oak Park Heights, MN 1 Wetland Delineation Report For: 1 Alan Catchpool, P.E., CPESC Department Leader CEI Engineering 2277 West Highway 36. Suite 200 Roseville, MN 55113 4 arrowhead environmen consulti 1 Wetland Consulting Services Performed by: 1 Ben Carlson, WDC ( #1125) AEC Project # 2010 -021 September 23, 2010 1 Arrowhead Environmental Consulting 2909 Meadow Lane Mound, MN 55364 1 TABLE OF CONTENTS 1 Project Overview: Summary of Project and Results ' Project Figures and Supporting Data: J g PP g 1 Figure 1: Project Location Map (USGS Topo) Figure 2: Project Location Map (MN DNR PWI) ' Figure 3: Washington County Soil Survey Figure 4: National Wetland Inventory Map Figure 5: Delineated Wetland Boundaries and Sample Locations (Approximate) 1 Field Data Collection Forms (Data Sheets) Soil Texture and Feature Guide ' Photo Log Report Body: 1 Introduction .1 ' Methods 1 Results .1 1 Discussion .2 Data Sources and Literature References 1 1 1 1 1 1 Project Overview ' On September 10, 2010, Arrowhead Environmental Consulting (AEC) performed a wetland delineation for the property located at: 1 No assigned address; the parcel is located south of 60 Street North and east of Norell Avenue North. The legal description of the parcel is: A part of the NE 1 /4 of Section 5, ' T29N, R2OW, Washington County, Oak Park Heights, Minnesota. The parcel is a total of 1.33 acres. ' • Two wetland basins were delineated within the parcel bounds • Wetlands 1 and 2 are not indicated on the NWI map; AEC classified both ' wetlands as Shallow Marsh (Type 3, PEMF) wetland • Neither wetland is indicated on the Minnesota Department of Natural Resources 1 Public Water Inventory Map (PWI) • The Crystal Lake (non - hydric) soil series is mapped within the location of ' Wetlands 1 and 2 • Wetlands 1 and 2 are dominated by reed canary grass, cattail, hummock sedge, and Kentucky blue grass ' • The boundaries for Wetlands 1 and 2 were placed along the vegetation transition zone and an abrupt topographic break ' • AEC believes that Wetlands 1 and 2 may have been incidentally created and may be exempt from mitigation 1 Wetland ID Classification Type NWI PWI # Wetland 1 Shallow Marsh Type 3, None None PEMF 1 Wetland 2 Shallow Marsh Type 3, None None PEMF 1 1 1 1 1 1 1 1 1 i Figures 1 1 1 1 1 1 1 1 1 1 1 .-. `:+ * "� Driving Park �` lil , i I Wild Pine Orleans -F' ( I -iw u �¢ f r e.� 110 1� t ■G 'I va 9 'fw loc...' `rlR. tom• l _ f ! 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I ,I," Map of Project Location Figure 2 7r Overlaid on MN DNR PWI Map /arrowhead Approximate Parcel Boudary environmental Q � � 'Feet CEI Engineering 1 c o n s u l t i n g 0 625 1.250 2.500 Oak Park Heights. MN o nett , * r oriett $� Barr B ar � °� ' ', , R . • .LL „, .ntICIC ;vim F s # `i Cry stal Lake ,� va G , p r , .,,, .... -> . . - 3 i i , .. e s 1 i - ll , 4 Antis , a :4:::; `4114k ,1",,,..4.- c f.t,:::771:46:, ;I'A., :*'"'/IA ' '' -,. . t' 'i -'',, w f 3 f 1 k Washington County Sail Survey Figure 3 Overlaid on ?004 Aerial Photo r�e� {.� o I (, 1 t Qwl ea� Non Hydric ��� / Hydric Ppproxirnate Parcel Bouda nv i (�YIIIienttl� AurtoZone iFeet CEI Engineering c {� r1 S ll 1 Y1 87 -5 350 Oak Park Heights MN 1 , 4 ' . ''�. sk 1 4 � •T ..,, , "--N-v V , r :'5. ' " e..+Y. =*. 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MN 1 1 1 1 1 i Supporting Data I Reset Form Print Form I WETLAND DETERMINATION DATA FORM — Midwest Region Project/Site: AutoZone City /County: Oak Park Heights, Washington Sampling Daze: 9/10/2010 I Applicant/Owner: CEI Engineering State: MN Sampling R2O Point: 1 -1 Wet Investigator(s): BPC (WDC #1125) Section, Township, Range: NE 1/4 of Sec. 5, T29N. W' Landform (hillslope, terrace, etc.): Basin Local relief (concave. convex. none): Concave I Slope ( %): 2 Lat: Long: Datum: Soil Map Unit Name: Crystal Lake NWI or WWI classification: None Are climatic / hydrologic conditions on the site typical for this time of year? Yes X No Of no, explain in Remarks.) I Are Vegetation Soil or Hydrology significantly disturbed? Are "Norma! Circumstances" present? Yes X No Are Vegetation Soil or Hydrology naturally problematic? (If needed, explain any answers in Remarks.) I SUMMARY OF FINDINGS — Attach site map showing sampling point locations, transects, important features, etc. Hydrophytic Vegetation Present? Yes X No Is the Sampled Area Hydric Soil Present? Yes X No within a Wetland? Yes X No I Wetland Hydrology Present? Yes X No Remarks: 1 VEGETATION — Use scientific names of plants. Absolute Dominant Indicator Dominance Test worksheet: Tree Stratum (Plot size: 30' ) % Cover Species? Status Number of Dominant Species I 1 • That Are OBL, FACW, or FAC: 2 (A) 2. 3 Total Number of Dominant Species Across At Strata: 2 (B) I 4. Percent of Dominant Species 5 ' That Are OBL. FACW. or FAC: 100 (NB) = Total Cover Sapling /Shrub Stratum (Plot size: 15' ) Prevalence Index worksheet: I 1 _ Total % Cover of: Multiply by: 2 - OBL species x 1 = 0 3 . FACW species x 2 = 0 I 4. 5 FAC species x 3 = 0 FACU species x 4 = 0 = Total Cover UPL species x 5 = 0 Herb Stratum (Plot size: 1m sq. ) I 1. Poa p,atensis 50 x FAC Column Totals: (A) 0 (6) 2. Carex str/cta 10 OBL Prevalence Index = BA = 0 3. Cirsium arvense 10 FACU i Hydrophytic Vegetation Indicators: I 4. Sonchus arvens/s 5 25 x FAC I X Dominance Test is >50 5. Typha anqustifo//a OBL Prevalence Index is 5 53.0 6. Phalaris arundinacea 10 FACW ` Morphological Adaptations (Provide supporting 7. data in Remarks or on a separate sheet) I 9 A Problematic Hydrophytic Vegetation' (Explain) 9. 10. Indicators of hydric soil and wetland hydrology must be present, unless disturbed or problematic. I 110 = Total Cover Woody Vine Stratum (Plot size: ) 1. Hydrophytic 2 Vegetation I Present? Yes X No = Total Cover Remarks: (Include photo rumbers here or on a separate sheet.; US Army Corps of Engineers Midwest Region — Interim Version 1 I 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 I (inches) Color (moist) % Color (moist) % Type Loc Texture Remarks 0 -10 7.5YR 412 100 7.5YR 4'6 5 C M SL 10 -24 10YR 4/2 100 7.5YR 4/6 5 C M SL 1 1 Type: C= Concentration, D= Depletion, RM= Reduced Matrix, CS =Covered or Coated Sand Grains. `Locatior: PL =Pore Lining, M= Matrix. I Hydric Soil Indicators: _ Prairie R Indicators for Problematic Hydric Soils Coast (Al) Sandy Gleyed Matrix (S4) Sandy (A16) Histic Epipedon (A2) T Sandy Redox (S5) _ Iron - Marganese Masses (F12) _ Black Histic (A3) _ Stripped Matrix (S6) _ Other (Explain in Remarks) I , Hydrogen Sulfide (A4) Stratified Layers (A5) _Loamy Mucky Mineral (F1) Loamy Gleyed Matrix (F2) _ 2 cm Muck (A10) X Depleted Matrix (F3) Depleted Below Dark Surface (Al 1) ` Redox Dark Surface (F6) I ' Thick Dark Surface (Al2) Dark Surface (F7) Redox Depressions (F8) 'Indicators of hydrophytic vegetation and Sandy Mucky Mineral (Si) wetland hydrology must be present, _ 5 crn Mucky Peat or Peat (S3) unless disturbed or problematic. Restrictive Layer (if observed): - I Type: Depth (inches): Hydric Soil Present? Yes X No Remarks: 1 I HYDROLOGY Wetland Hydrology Indicators: I Primary Indicators (minimum of one is required; check all that apply) Secondary Indicators (minimum of two required) Surface Water (A1) Water- Stained Leaves (89) Surface Soil Cracks (86) _ High Water Table (A2) _Aquatic Fauna (B13) _ Drainage Patterns (810) _ Saturation (A3) _ True Aquatic Plants (B14) — Dry- Season Water Table (C2) I — Water Marks (B1) Sediment Deposits (82) — Hydrogen, Sulfide Odor (C1) Crayfish Burrows (C8) Oxidized Rhizospheres on Living Roots (C3) Saturation Visible on Aerial Imagery (C9) X Drift Deposits (B3) _ Presence of Reduced Iron (C4) Stunted or Stressed Plarts (D1) Algal Mat or Crust (B4) _ Recent Iron Reduction in Tilled Soils (C6) X Geomorphic Position (D2) I _ Iron Deposits (B5) _ Thir Muck Surface (C7) X FAC Neutral Test (D5) Inundation Visible on Aerial Imagery (B7) _ Gauge or Well Data (D9) Sparsely Vegetated Concave Surface (B8) Other (Explain in Remarks) I Field Observations: Surface Water Present? Yes No X Depth (inches): Water Table Present? Yes No X Depth (inches): Saturation Present? Yes X No Depth (inches): 16 " Wetland Hydrology Present? Yes X No I (includes capillary fringe) Describe Recorded Data (stream gauge, monitoring well, aerial photos, previous inspections), if available: Remarks: 1 US Army Corps of Engineers Mirwest Region – Interim Version 1 Reset Form 1 Print Form 1 WETLAND DETERMINATION DATA FORM — Midwest Region Project/Site: AutoZane City /County: Oak Park Heights, Washington Sampling Date: 9/10/2010 I Applicant/Owner: CEI Engineering State: MN Sampling Point: 1 -1 Up Investigator(s): BPC (WDC #1125) Section. Township, Range: NE 1/4 of Sec. 5, T29N, R20W Landform (hilisiope, terrace, etc.): Slope Local relief (concave, convex, none): Concave I Slope ( %): 2 Lat: Long: Datum: Soil Map Unit Name: Crystal Lake NWI or WWI classification: None Are climatic / hydrologic conditions on the site typical for this time of year? Yes X No (If no, explain in Remarks.) I Are Vegetation or Hydrology significantly disturbed? Are "Normal Circumstances" present? Yes X No Are Vegetation Soil or Hydrology naturally problematic? (If needed, explain any answers in Remarks.) I SUMMARY OF FINDINGS — Attach site map showing sampling point locations, transects, important features, etc. Hydrophytic Vegetation Present? Yes No X Is the Sampled Area Hydric Soil Presert? Yes No X within a wetland? Yes No X I Wetland Hydrology Present? Yes No X Remarks: 1 VEGETATION — Use scientific names of plants. Absolute Dominant Indicator Dominance Test worksheet: Tree Stratum (Plot size: 30' ) % Cover Species? Status Number of Dominant Species I 1. That Are OBL. FACW. or FAC: 1 (A) 2 Total Number of Dominant 3. Species Across All Strata: 2 (B) I 4. Percent of Dominant Species 5. That Are OBL. FACW, or FAC: 50 (NB) = Total Cover Sapling /Shrub Stratum (Plot size: 15' ) Prevalence Index worksheet: I 1. Total % Cover of. OBL species P4uitipIy by: 2. x 1 = 0 3. FACW species x 2 = 0 I 4. FAC species x 3 = 0 5. FACU species x 4 = 0 = Total Cover UPL species x 5 = 0 Herb Stratum (Plot size: 1m sq. ) I Column Totals: (A) 0 (6) 1. Poa pratensis 80 X FAC 2. Cirsium an tense 25 X FACU Prevalerce Index = B/A = 0 3. Sonchus arvensis 5 FAC Hydrophytic Vegetation Indicators: I 4. — Dominance Test is >50% 5. Prevalence Index is 5 6. , Morphological Adaptations' (Provide supporting 7. data in Remarks or or a separate sheet) I 8. _ Problematic Hydrophytic Vegetation (Explain) 9. Indicators of hydric soil and wetland hydrology must 10. be present, unless disturbed or probiematic. 110 = Total Cover Woody Vine Stratum (Plot size: 1. Hydrophytic 2 Vegetation 1 Present? Yes No X = Total Cover 1 Remarks: (Include photo numbers here or on a separate sheet.) 1 US Army Corps of Engineers Midwest Region — Interim Version 1 1 1 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 I (inches) Color (moist) % Color (moist) % Type Loc Texture Remarks 0 8 10YR 3/2 100 SL 8 -24 10YR 3/1 100 7.5YR 3/4 5 C M Loam 1 1 Type: C= Concentration, D= Depletion, RM= Reduced Matrix, CS= Covered or Coated Sand Grains `Location: PL =Pere Lining, M= Matrix. _ I Hydric Soil Indicators: _ Histosol (Al) Sandy Gleyed Matrix (S4) Indicators for Problematic Hydric Solis': Coast Prairie Redox (A16) _ Histic Epipedon (A2) Sandy Redox (S5) _ Iron - Marganese Masses (F12) Black Histic (A3) Stripped Matrix (S6) _ Other (Explain in Remarks) I = Hydrogen Sulfide (A4) = Loamy Mucky Mineral (F1) Stratified Layers (A5) Loamy Gleyed Matrix (F2) 2 cm Muck (A10) _ Depleted Matrix (F3) _ Depleted Below Dark Surface (Al 1) _ Redox Dark Surface (F6) I = Thick Dark Surface (Al2) ^ Depleted Dark Surface (F7) Redox Depressions (F8) Indicators of hydrophytic vegetation and Sandy Mucky Mineral (S1) wetlard hydrology must be present. _ 5 cm Mucky Peat or Peat (S3) unless disturbed or problematic. Restrictive Layer (if observed): 1 Type: Depth (inches): Hydric Soil Present? Yes No X Remarks: 1 1 HYDROLOGY Wetland Hydrology Indicators: I Primary Indicators (minimum of one is required; check all that apply) Secondary Indicators (minimum of two required) Surface Water (Al) Water- Stained Leaves (69) Surface Soil Cracks (66) _ High Water Table (A2) _ Aquatic Fauna {613) _ Drainage Patterns (B10) _ Saturation (A3) _ True Aquatic Plants (B14) _ Dry-Season Water Table (02) I ` Water Marks (81) Sediment Deposits (82) ! Hydrogen Sulfide Odor (C1) _Crayfish Burrows (08) Oxidized Rhizospheres on Living Roots (C3) _ Saturation Visible or Aerial Imagery (C9) _ Drift Deposits (83) _ Presence of Reduced Iron (C4) ` Stunted or Stressed Plants (D1) _ Algal Mat or Crust (B4) Recent Iron Reduction in Tilled Soils (C6) , Geomorphic Position (D2) 1 _ Iron Deposits (95) _ Thin Muck Surface (07) _ FAC- Neutral Test (D5) _ Inundation Visible or Aerial Imagery (B7) _ Gauge or Well Data (D9) _ Sparsely Vegetated Concave Surface (B8) _ Other (Explain in Remarks) I Field Observations: Surface Water Present? Yes No X Depth (inches): Water Table Present? Yes No X Depth (inches): I { Saturation Present? Yes No X Depth (inches): Wetland Hydrology Present? Yes No X (includes capillar _fringe) Describe Recorded Data (stream gauge, monitoring well, aerial photos, previous inspectiors), if available: 1 Remarks: 1 US Army Corps of Engineers Midwest Region — Interim Version 1 1 Reset Form Print Form 1 WETLAND DETERMINATION DATA FORM — Midwest Region Project/Site: AutoZone City /County: Oak Park Heights, Washington Sampling Date: 9/10 /2010 I Applicant/Owner: CEI Engineering State: MN Point: 2 -1 Wet Investigators }: BPC (WDC #1125) Section, Township, Range: NE 1/4 /4 of Sec. 5, T29N, R20W Landform (hiilsiope, terrace, etc.): Basin Local relief (concave, convex, none): Concave I Slope ( %): 5 Lat: Long: Datum: Soil Map Unit Name: Crystal Lake NWI or' WWI classification: None Are climatic / hydrologic conditions on the site typical for this time of year? Yes X No (If no, explain in Remarks.) I Are Vegetation or Hydrology significantly disturbed? Are "Normal Circumstances" present? Yes X No Are Vegetation Soii or Hydrology naturally problematic? (If needed, explain any answers in Remarks.) I SUMMARY OF FINDINGS — Attach site map showing sampling point locations, transects, important features, etc. Hydrophytic Vegetation Present? Yes X No Hydric Soil Presert? Yes X No Is the Sampled Area I Wetland Hydrology Present? Yes X No within a Wetland? Yes X No Remarks: 1 VEGETATION — Use scientific names of plants. Absolute Dominant Indicator Dominance Test worksheet: Tree Stratum (Plot size: 30' ) % Cover Species? Status Number of Dominant Species I 1. 2. That Are OBL, FACW. or FAC: 2 (A; 3 Total Number of Dominant Species Across All Strata: 2 (B)) I 4. 5 Percent of Dominant Species That. Are OBL. FACW, or FAC: 100 (NB) = Total Cover Sapling /Shrub Stratum (Plot size: 15' ) Prevalence Index worksheet: I 1. Total °;; Cover of: OBL species x 1 fvluitiply by: 2. = 0 3. FACW species x 2 = 0 I 4. 5. FAC species x 3 = 0 FACU species x 4 = 0 = Total Cover UPL species x 5 = 0 Herb Stratum (Plot size: 1m s::. ) 1 1. Typha anqustifolia 70 X OBL Column Totals: (A) 0 (B) 2. Pnaians arundinacea 30 X FACW Prevalence Index = B!A = 0 3. Hydrophytic Vegetation Indicators: I 4. 5. __ X Domirance Test is >50% Prevalence Index is 5 53.0 6. _ Morphological Adaptations (Provide supporting 7 data in Remarks or on a separate sheet) I 8. _ _ Problematic Hydrophytic Vegetation' (Explain) 9. 10. Indicators of hydric soil and wetland hydrology must be present, unless disturbed or problematic. I Woody Vine Stratum (Plot size: ) 100 = Total Cover 1. Hydrophytic 2 Vegetation Present? Yes X No 1 = Total Cover Remarks: (Include photo numbers here or on a separate sheet.) 1 US Arrny Corps of Engineers Midwest Region - Interim Version 1 1 I SOIL sampling Point: 2-1 Wet Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of indicators ") Depth Matrix Redox Features I (inches) Color (moist) % Color (moist) % Type' Loc' Texture Remarks 1 1 'Type: C= Concentration, D= Depletion, RM= Reduced Matrix, CS= Covered or Coated Sand Grains. `Location: PL =Pore Lining, M= Matrix. I Hydric Soil Indicators: Histosol (Al) Sardy Gleyed Matrix (S4) Indicators for Problematic Hydric Soils': Coast Prairie Redox (A16) Histic Epipedon (A2) Sardy Redox (S5) _ Iron- Manganese Masses (F12) _ Black Histic (A3) _ Stripped Matrix (S6) X Other (Explain in Remarks) I T Hydrogen Sulfide (A4) = Loamy Mucky Mineral (F1) Stratified Layers (A5) Loamy Gleyed Matrix (F2) _ 2 cm Muck (A10) _ Depleted Matrix (F3) Depleted Below Dark Surface (Al 1) Redox Dark Surface (F6) I + Thick Dark Surface (Al2) = Depleted Dark Surface (F7) Redox Depressions (F8) 'Indicators of hydrophy?ic vegetation and Sandy Mucky Mineral (Si) wetland hydrology must be present. _ 5 cm Mucky Peat or Peat (S3) unless disturbed or problematic. Restrictive Layer (if observed): I Type: Depth (inches): Hydric Soil Present? Yes X No Remarks: I Hydric soil assumed, OBL and FACVW vegetation present, abrupt boundary, standing water present in ditch/wetland. I HYDROLOGY Wetland Hydrology Indicators: I Primary Indicators (minimum of one is required; check all that apply) Secondary indicators (minimum of two required) X Surface Water (A1) Water - Stained Leaves (89) Surface Soil Cracks (B6) High Water Table (A2) Aquatic Fauna (813) _ Drainage Patterns (B10) Saturation (A3) _ True Aquatic Plants (B14) _ Dry - Season Water Table (C2) I ' Water Marks (B1) Sediment Deposits (82) — Hydrogen Sulfide Odor (C1) _ Crayfish Burrows (C8) Oxidized Rbizospheres on Living Roots (C3) _ Saturation Visible on Aerial Imagery (C9) Drift Deposits (B3) _ Presence of Reduced Iron (C4) _ Stunted or Stressed Plants (D1) I Algal Mat or Crust (84) — Recent Iron Reduction in Tilled Soils (C6) X Geomorphic Position (D2) Iron Deposits (B5) Thin Muck Surface (C7) X FAC- Neutral Test (D5) Inundation Visible or Aerial Imagery (87) _ Gauge or Well Data (D9) Sparsely Vegetated Concave Surface (88) _ Other (Explain in Remarks) I Field Observations: - Surface Water Present? Yes X No Depth (inches): 1„ Water Table Present? Yes X No Depth (inches): I Saturation Present? Yes X No Depth (inches): Wetland Hydrology Present? Yes X No (includes capillary fringe) Describe Recorded Data (stream gauge, monitoring well, aerial photos. previous inspections), if available: 1 Remarks: 1 US Army Corps of Engineers Midwest Region - Interim Version 1 I Reset Form 1 , Print Form 1 WETLAND DETERMINATION DATA FORM — Midwest Region Project/Site: AutoZone City/County: ak Park Heights, Washin ton y ty: g g Sampling Date: 9/10/2010 I Applicant/Owner: CEI Engineering Section, Township, State: MN Sampling Point: 2 -1 Up Irvestigator(s): BPC (WDC #1125) Secti Townshi Range: NE 1/4 of Sec. 5, T29N, R20W Landform (hillsiope, terrace, etc.): Slope Local relief (concave, convex, nore: Concave I Slope ( %): 5 Lat: _ Long: Datum: Sot! Map Unit Name: Crystal Lake NWi or WWI classification: None Are climatic / hydrologic conditions or the site typical for this time of year? Yes X No (If no, explain in Remarks.) I Are Vegetation or Hydrology significantly disturbed? Are "Normal Circumstances" present? Yes X No Are Vegetation Soil or Hydrology naturally problematic? (If needed, explain any answers in Remarks.) SUMMARY OF FINDINGS — Attach site map showing sampling point locations, transects, important features, etc. 1 Hydrophytic Vegetation Present? Yes No X Is the Sampled Area Hydric Soil Presert? Yes No X within a Wetland? Yes No X Wetland Hydrology Present? Yes No X 1 Remarks: 1 VEGETATION — Use scientific names of plants. Absolute Dominant Indicator Dominance Test worksheet: Tree Stratum (Plot size: 30' ) % Cover Species? Status Number of Dominant Species I 1 That Are OBL. FACW, or FAC: 1 (A) 2. 3 Total Number of Dominant Species Across All Strata: 3 (6) 4. I 5 Percent of Dominant Species That Are OBL. FACW, or FAC: 33 (A/B) = Total Cover Sapling /Shrub Stratum (Plot size: 15' Prevalence Index worksheet: I 1 . % Cover of: Multiply by: 2. OBL species x 1 = 0 3. FACW species x 2 = 0 I 4. FAC species x 3 = 0 5. FACU species x 4 = 0 = Total Cover UPL species x 5 = 0 Herb Stratum (Plot size: 1m sq. ) Column Totals: (A) 0 (5) I 1. Poa prafensis 50 X FAC 2. Bromus inermis 20 X UPL Prevalerce Index = BIA = 0 3. Sotidago canadensis 30 X FACU Hydrophytic Vegetation Indicators: I 4. _ _ Dominance Test is >50% 5. Prevalence Irdex is 53.0 6. _ Morphological Adaptations (Provide supporting 7 data in Remarks or or a separate sheet) I 8. _ Problematic Hydrophytic Vegetation (Explain.) 9. 10. Indicators of hydric soil and wetland hydrology must be present. unless disturbed or problematic. ' Woody Vine Stratum (Plot size: 1. 100 = Total Cover Hydrophytic 2 Vegetation I Present? Yes No X = Total Cover Remarks: (Include photo numbers here or or a separate sheet.) US Amiy Corps of Engineers Midwest Region — Interim Version 1 I SOIL Sampling Point: 2 -1 Up Profile Description: (Describe to the depth needed to document the indicator or confirm the absence of indicators.) Depth Matrix Redox Features 1 (inches) Color (moist) % Color (moist) % Type' Loc` Texture Remarks 1 1 Type: C= Concentration, D= Depletion, RM= Reduced Matrix, CS= Covered or Coated Sand Grains `Location: PL =Pore Lining, M= Matrix, I Hydric Soil Indicators: — Histosoi (Al) Sandy Gleyed Matrix (S4) Indicators for Problematic Hydric Solis': Coast Prairie Redox (A16) _ Histic Epipedon (A2) _ Sandy Redox (S5) Iron - Manganese Masses (F12) Black Histic (A3) , Stripped Matrix (S6) — Other (Explain in Remarks) I — Hydrogen Sulfide (A4) Stratified Layers (A5) = Loamy Mucky Mineral (F1) Loamy Gleyed Matrix (F2) 2 cm Muck (A10) — Depleted Matrix (F3) Depleted Below Dark Surface (Al 1) _ Redox Dark Surface (F6) I = Thick Dark Surface (Al2) = Depleted Dark Surface (F7) Redox Depressions (F8) Indicators of hydrophytic vegetation and Sandy Mucky Mineral (Si) wetland hydrology must be present. 5 cm Mucky Peat or Peat (S3) unless disturbed or problematic. Restrictive Layer (if observed): 1 Type: Depth (inches): Hydric Soil Present? Yes No X Remarks: I Nor-Hydric soil assumed, UPL and FACU vegetation present, abrupt boundary. 1 HYDROLOGY Wetland Hydrology Indicators: I Primary Indicators (minimum of one is required; check all that apply) Secondary Indicators (mirimum of two required) Surface Water (A1) Water- Stained Leaves (B9) Surface Soil Cracks (86 High Water Table (A2) _Aquatic Fauna (613} _ Drainage Patterns (810) _ Saturation (A3) _ True Aquatic Plants (B14) _ Dry- Season Water Table (C2) I — Water Marks (B1) Sediment Deposits (B2) Hydrogen Sulfide Odor (C1) _Crayfish Burrows (08) Oxidized Rhizospheres on Living Roots (C3) — Saturation Visible on Aerial Imagery (09) Drift Deposits (B3) Presence of Reduced Iron (C4) _ Stunted or Stressed Plants (01) _ Algal Mat or Crust (B4) ` Recent Iron Reduction in Tilled Soils (06) _ Geomorphic Position (D2) I Iron Deposits (85) Thin Muck Surface (C7) _ FAC- Neutral Test (05) _ Inundation Visible on Aerial Imagery (B7) — Gauge or Well Data (D9) Sparsely Vegetated Concave Surface (88) _ Other (Explain in Remarks) I Field Observations: Surface Water Present? Yes No X Depth (inches): Water Table Present? Yes No X Depth (inches): I Saturation Present? Yes No X Depth (inches): Wetland Hydrology Present? Yes No X (includes capillary fringe) Describe Recorded Data (stream gauge, monitoring well, aerial photos, previous inspections), if available: 1 Remarks: Abrupt wetland /ditch boundary. 1 ' US Army Corps of Engineers Midwest Region – Interim Version 1 1 1 Soil Texture and Feature Guide 1 TEXTURES 1 LS Loamy Sand An "F" modifier in front of any sandy soil texture ' SL Sandy Loam abbreviation ( "S ") represents "Fine" ie. Loam Loam FSL or FLS. SiL Silt Loam SCL Sandy Clay Loam CL Clay Loam ' SiCL Silty Clay Loam 1 SC Sandy Clay Clay Clay ' Sic Silty Clay 1 FEATURES F few F F very F faint C common M medium D distinct M many C coarse P prominent VC very coarse IOSM Iron Oxide Sof t Masses ORC Oxidized Root Channels DPL Depletions 1 1 1 1 . , . e t 1 T- ti 1 x I , kP s it rte-' .y.,.».r- o ' "`- �` . P 1 • • r Photo 1: View of Wetland 1 facing north from the southern edge. on we so 4�lYfaiue �. ._.. � r � s J ,. t ; - . r l . 1 ^fie ' to 3} ' } E' Y rE p e � { 1 41 • iG s ' JY 5 .' d F ° , i i, z �} , � a „,,o- , X 11 , . I 1 1 , .,, -.. ” 2a .�� ,., *n P -.1:1O .... to 2: View of Wetland 1 edge at transect 1 -1 location. 1 • L ., 4 ,, • 4. $414 ,,,,,,,,..„, 1 pwi , -1 t , , , ,, „., , . 1 . , .., . . <r i ,art � ,f.',r . � ' � 7 ) i A ,1- k I t 3+' � JF 9A��444 ;/,'''' � + tj- i pk 4'x .+FNp ,, -4: yi�t 4 s i .'1 {i 1 ° Map 4 .. i� .ra° K : ,d F y W r , :, F r f' b S .4>` r' Photo 3: View of Wetland 2 facing east from the western edge. I wr _- r " z tl 4 I , , , , ..,.4„, .,,, .. , , " ,, 1 ,,, __ ! 7 ,:.',.. . .„;t1.7... :^:, ,_ ..,. , „,....!,,,,,,,:„..' r...—...t■ , *,,, _, "'NV' — ' 4.4t • - ' 4. '4 ;. � ate : 1 F * ,�'.'„�. •o, C�;yt a z }: },e ,� ` 44 �z� 1 aw �'f';3 �r ' F E � � i� � � q � � ''' , „1;,-.4-;.; f K " r4 � 1 � *^ , fi 'per °$ " y fi. ' ii 4 * de 4 :. k ''',... ' r- ce$ i .k . - 04.‘trlit ,t i r:rr ; e 4t r - -: , • -7 .,4 , ..4., -,,, ,, „ ; , ..:::: , , , :. - ----...,,g-4,,.. - A-...' , Photo 4: Typical view of the upland area. 1 1 Introduction ' On September 10, 2010, Arrowhead Environmental Consulting (AEC) performed a wetland delineation for the property located at: 1 No assigned address; the parcel is located south of 60 Street North and east of Norell Avenue North. The legal description of the parcel is: A part of the NE 1 /a of Section 5, ' T29N, R20W, Washington County, Oak Park Heights, Minnesota. The parcel is a total of 1.33 acres. Methods AEC utilized the 1987 US Army Corps of Engineers Wetlands Delineation Manual and ' Midwest Regional Supplement to perform the wetland delineation. A United States Geological Survey (USGS) Map (Stillwater Quad) (Figure 1), the Minnesota Department of Natural Resources (MN DNR) Public Water Inventory (PWI) Map (Figure 2), the ' Washington County Soil Survey Map (Figure 3), and the National Wetland Inventory (NWI) Map (Figure 4) were reviewed prior to the site visit and used in the delineation process. The delineated wetland boundaries (approximate) are indicated on Figure 5 and are overlaid on a 2004 aerial image. AEC used the routine delineation method. ' Wetland classification followed methods described by the USACOE - St. Paul District; Eggers and Reed "Wetland Plants and Plant Communities of MN and WI ". The Circular 39 and Cowardin et al. classifications are given as well. The indicator status of plants ' was determined using the National List of Plant Species That Occur in Wetlands — Region 3 (Sabine 1999). In accordance with the Midwest Regional Supplement, the + and — have been removed from the vegetation indicator status. Pink pinflags were used to delineate the wetlands and were numbered sequentially. Sample points were taken to document the vegetation, soils, and hydrology indicators 111 within representative upland and wetland locations. Results Office Results Wetlands 1 and 2 are not indicated on the NWI or PWI maps. The Crystal Lake (non - 1 hydric) soil series is mapped within the area of Wetlands 1 and 2. Field Results Wetland 1 Wetland 1 is described as a Shallow Marsh (Type 3, PEMF) wetland. Wetland 1 is ' primarily dominated by reed canary grass (Phalaris arundinacea), hummock sedge (Carex stricta), cattail (Typha spp.), and Kentucky bluegrass (Poa pratensis). The adjacent upland area is dominated by Kentucky bluegrass, Canada thistle (Cirsium 1 1 arvense), common milkweed (Asclepias syriaca), and Canada goldenrod (Solidago canadensis). The wetland boundary was placed along the vegetation transition zone; there was an abrupt shift in vegetation between the reed canary grass and sedge (hydrophytic) and the Canada thistle and common milkweed (non - hydrophytic). Kentucky bluegrass was observed in both the wetland and upland areas (Kentucky bluegrass was formerly FAC- and non - hydrophytic under the original 1987 manual). A moderate to abrupt topographic ' break was observed along the wetland boundary; the boundary was placed at or near mid - slope. The wetland sample point met the F3 (Depleted Matrix) hydric soil indicator, the upland soil did not meet a hydric soil indicator. Additionally, soil was saturated at 16" ' below the surface at the wetland sample point; the soil was dry at the upland sample point. Wetland 2 Wetland 2 is described as a Shallow Marsh (Type 3, PEMF) wetland. Wetland 2 is primarily dominated by reed canary grass and cattail. The adjacent upland is dominated by Kentucky bluegrass, smooth brome (Bromus inermis), common milkweed, and Canada goldenrod. The wetland boundary was placed along the vegetation transition zone; there was an abrupt shift in vegetation between the reed canary grass and cattail (hydrophytic) and the Canada goldenrod and Kentucky bluegrass (non - hydrophytic). An abrupt topographic break was observed along the wetland boundary; the boundary was placed at or near mid - slope. Soil samples were not taken as the wetland boundary was abrupt, FACW and OBL vegetation was dominant and standing water was observed within the basin; hydric soils were assumed. It is likely that Wetlands 1 and 2 were incidentally created and may be exempt from mitigation. Wetland 1 is a narrow ditch running along the eastern edge of a bituminous parking lot. Much (if not all) of the runoff from the adjacent building and parking lot ' drains into Wetland 1; it is likely that Wetland 1 was dredged to channel runoff from the parking lot to the north and developed wetland characteristics over time. Wetland 2 is likely incidental as well; there is a large culvert at the east end of Wetland 2 that discharges runoff (into Wetland 2) from the properties to the east and drains to the west. AEC noted water from Wetlands 1 and 2 drains to the west and off of the subject property. 1 Discussion 1 Two wetland basins were delineated within the subject parcel. Both wetlands are described as Shallow Marsh (Type 3, PEMF) wetland dominated by reed canary grass, 1 hummock sedge, cattail, and Kentucky bluegrass. Wetland 1 was delineated by approximately 14 flags; Wetland 2 was delineated by approximately 12 flags. 1 r 2 1 I In order to be official the wetland delineation must be reviewed and approved by the Local Government Unit (LGU) and potentially other agencies (Local, State, Federal). 1 AEC recommends that the wetland boundary be located by a Professional Land Surveyor or located by a survey grade GPS unit. Any work within or adjacent to a wetland will require Wetland Conservation Act (WCA) permits (and potentially other permits). Please 1 consult with AEC if you plan on filling, draining, excavating wetlands within your project location. If you have any questions regarding this report or any questions about our services please feel free to contact Ben Carlson at any time (612- 237 - 5996). I Thank you, Ben Carlson 1 Ben Carlson, WDC Ecologist/Owner I Arrowhead Environmental Consulting 1 1 1 1 1 1 1 1 1 1 1 1 3 1 1 Data Sources: USGS Quadrangle Map — Stillwater 7.5- Minute Quadrangle, Minnesota, U.S.A. I Minnesota Department of Natural Resources Protected Waters Inventory Map, Washington County 1985 (Revised 1996 data from the Mn DNR Data Deli, online). I Soil Survey of Washington County. U.S.D.A. Data obtained from the NRCS /SSURGO website. I United States Fish and Wildlife Service National Wetland Inventory Map — Stillwater Quadrangle. 1991. I Aerial Photos were obtained from the Land Management Information Center (LMIC) Website (WMS Server) I Literature Referenced/Technical Documents: Environmental Laboratory. 1987. 1987 U.S. Army Corps of Engineers Wetlands Delineation I Manual. Technical Report Y -87 -1, US Army Engineer Waterways Experiment Station, Vicksburg, Mississippi. I U.S. Army Engineer Research and Development Center. 2007. Regional Supplement to the Corps of Engineers Wetland Delineation Manual: Midwest Region. US Army Engineer Waterways Experiment Station, Vicksburg, Mississippi. 1 Eggers, Steve D. and Donald M. Reed. 1997. Wetland Plants and Plant Communities of Minnesota and Wisconsin. US Army Corps of Engineers, St. Paul District. 263pp, I unclassified. Shaw, S.P., and C.G. Fredine. 1956. Wetlands of the United States. U.S. Fish and Wildlife I Service, Circular 39. 67pp. 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. Sabine, B. J. 1999. National List of Plant Species that Occur in Wetlands: Region 3 — North I Central (Indiana, Illinois, Iowa, Michigan, Minnesota, Missouri, Wisconsin). Resource Management Group, Inc. 77pp. I USDA Soil Conservation Service, Washington, D.C., Misc. 2006. Field indicators of Hydric Soils in the United States. A guide for Identifying and Delineating Hydric Soils, Version 6.0 1 National Technical Committee for Hydric Soils. 1991. Hydric Soils of the United States. USDA Soil Conservation Service, Washington, D.C., Misc. Publication Number 1491. 1991. i 1 1 4