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HomeMy WebLinkAbout20250089 247 Kaydeross Ave East Final Subdivision SWPPP studloA Landscape Architecture+Engineering,DPC STORMWATER POLLUTION PREVENTION PLAN 247 Kaydeross Avenue East Saratoga Springs, NY April 4, 2024 *********************** OWNER: Frank Scarpinato 247 Kaydeross Ave East Saratoga Springs, NY 12866 Contractor: To be determined PREPARED BY: Studio A Landscape Architecture+ Engineering, D.P.C. 74 Warren Street Saratoga Springs, NY 12866 38 High Rock Ave,Suite 3 1 P.O.Box 272 1 Saratoga Springs, NY 12866 1 518.450.4030 TABLE OF CONTENTS DESCRIPTION OF EXISTING SITE....................................................................................... P. 1 DESCRIPTION OF EXISTING SOILS .................................................................................... P. 1 DESCRIPTION OF PROPOSED DEVELOPMENT ............................................................... p. 2 CONSTRUCTION PHASING .............................................................................................. p. 2 POLLUTION PREVENTION MEASURES ............................................................................ p. 2 SEDIMENTATION AND EROSION CONTROL ................................................................... p. 2 RETENTION OF RECORDS ................................................................................................... p. 3 APPENDCIES A PROJECT LOCATION MAP B USDA SOIL SURVEY C EROSION AND SEDIMENT CONTROL DRAWINGS DESCRIPTION OF EXISTING SITE The project site is located at 247 Kaydeross Ave East, Chester, NY, south of Crescent Ave and east of the Adirondack Northway(Tax Map ID: 179.-3-29.211).The lot is approximately 13.35- acres in size and is located within the Rural Residential (RR) zoning district as designated by the City of Saratoga Springs.This property is currently developed with a single family residence, access drive, and various accessory structures such as greenhouses, a garage, and a shed.The property also contains a small agricultural field and a small portion of a wetland.The remainder of the site is wooded. A ridge runs through the center of the site from the southwest to northeast,where the residence is located.The site slopes back to Kaydeross Avenue East at approximately a 10% slope. The other side of the ridge slopes back to Cresent Avenue at slopes exceeding 25%.This portion of the site is not proposed to be developed. DESCRIPTION OF EXISTING SOILS The United States Department of Agriculture (USDA) Soil Survey obtained from the Natural Resource Conservation Service website indicates the surficial soil types on the property to be 90.7% Bernardston silt loam, at slopes from 3 to 25%(BmB through BmD) and 9.3% Pittstown silt loam, 3 to 8 percent slopes (PwB). The BmB through BmD series is identified by the USDA as hydrologic soil group (HSG) "C/D". These soils exhibit characteristics of HSG "C" when drained, which have a moderate runoff potential. When saturated these soils exhibit characteristics of soil group "D" which typically has a high runoff potential.These soils typically consist of silt loam. The PwB series is identified by the USDA as hydrologic soil group (HSG) "C/D".These soils exhibit characteristics of HSG "C" when drained, which have a moderate runoff potential. When saturated these soils exhibit characteristics of soil group "D"which typically has a high runoff potential.These soils typically consist of silt loam,transitioning to a gravelly loam deeper on the soil profile. DESCRIPTION OF PROPOSED DEVELOPMENT The parcel is proposed to be subdivided into 3 lots,with one of the lots containing permeant conservation easement areas and the existing single-family residence. The remaining two lots are proposed to be developed with a single-family residence. An access drive will be constructed to provide access to the two proposed lots on the western side of the parcel. Potable water service lines will be extended from a watermain under crescent avenue and wastewater will be treated with on-site systems. Anticipated disturbance areas, pervious and impervious areas are as follows: Disturbance Area ±110,904 ftZ Impervious (existing/proposed) ±16,900 ft2/±33,733 ftZ Pervious (existing/proposed) ±565,454 ftZ/±548,621 ftZ - 1 - CONSTRUCTION PHASING The project is anticipated to be completed in one phase.Areas subject to disturbance will be cleared and grubbed to accommodate the proposed development. Prior to clearing and grubbing operation, all erosion and sediment control measures indicated on the attached drawings shall be in place.The proposed access drive will be constructed up to the furthest lot. The drive will be completed upon construction of the adjacent road that will be tied into. Construction of the single family residences will occur based upon buyer demand. POLLUTION PREVENTION MEASURES Any litter on site, including construction debris,will be picked up each day and disposed of into solid waste containers. The contractor shall provide an approved secondary containment system for all fuel and petroleum temporarily stored on site. All vehicles on site will be monitored for leaks and receive regular preventative maintenance to reduce the chance of mechanical fluid leakage. During the placement of concrete for the building foundations, measures will be taken to ensure that fresh concrete does not enter any defined drainage paths and a concrete washout area will be provided by the contractor in accordance with the construction drawings. SEDIMENTATION AND EROSION CONTROL Prior to commencing any land clearing, silt fences will be installed in accordance with the construction drawings to collect silt from construction runoff. A stabilized temporary construction entrance will be installed at the location indicated on the construction drawings required for use by all construction traffic entering and leaving the site.The contractor is required to maintain the silt fences,temporary construction entrances and other applicable erosion and sediment control practices throughout the construction period. All exposed surfaces not covered with paving, structures, and similar finished surfaces will be covered with topsoil and seeded to establish a turf covering or will be landscaped and mulched. The areas receiving seed will be mulched to minimize erosion. Silt fences shall be installed downslope of the newly seeded areas. All erosion control measures shall be maintained and replaced, as required, during the course of construction until a well-established growth of turf is established. Silt fence shall be replaced as required during the course of construction until a well-established vegetative cover is established. Erosion and sediment control measures shall be inspected daily by a trained contractor as defined in Appendix A of the New York State Department of Environmental Conservation SPDES General Permit for Stormwater Discharges from Construction Activity Permit No. GP-0-20-001. Construction inspections shall be conducted in accordance with Part IV.B of GP-0-20-001. RETENTION OF RECORDS The contractor shall maintain a copy of this Storm Water Pollution Prevention Plan (SWPPP) at the project site. In addition,the contractor shall maintain a site logbook which will contain all -2 - storm water and erosion control inspection reports to be prepared by the trained contractor. A current copy of the construction drawings shall also be kept in the logbook with comments that may have been added by the trained contractor. SWPPP Report Prepared by: Matthew E. Huntington, PE Principal For Studio A I Landscape Architecture+ Engineering -3 - APPENDIX A Project Location Map ti � J 45 ! r , .......... � w. FiLj LAKE LONELY L } r, PROJECT SITE ' 1 cn r o - Iw jr •"R 10 r APPENDIX B USDA SOIL SURVEY USDA United States A product of the National Custom Soil Resource Department of Cooperative Soil Survey, Agriculture a joint effort of the United Report for N RCS States Department of Agriculture and other Saratoga Federal agencies, State Natural agencies including the Resources Agricultural Experiment County, New Conservation Stations, and local Service participants York 1. 0 400 ft February 14, 2024 Preface Soil surveys contain information that affects land use planning in survey areas. They highlight soil limitations that affect various land uses and provide information about the properties of the soils in the survey areas. Soil surveys are designed for many different users, including farmers, ranchers, foresters, agronomists, urban planners, community officials, engineers, developers, builders, and home buyers. Also, conservationists, teachers, students, and specialists in recreation, waste disposal, and pollution control can use the surveys to help them understand, protect, or enhance the environment. Various land use regulations of Federal, State, and local governments may impose special restrictions on land use or land treatment. Soil surveys identify soil properties that are used in making various land use or land treatment decisions. The information is intended to help the land users identify and reduce the effects of soil limitations on various land uses. The landowner or user is responsible for identifying and complying with existing laws and regulations. Although soil survey information can be used for general farm, local, and wider area planning, onsite investigation is needed to supplement this information in some cases. Examples include soil quality assessments (http://www.nres.usda.gov/wps/ portal/nres/main/soils/health/) and certain conservation and engineering applications. For more detailed information, contact your local USDA Service Center (https://offices.sc.egov.usda.gov/locator/app?agency=nres)or your NRCS State Soil Scientist(http://www.nres.usda.gov/wps/portal/nres/detail/soils/contactus/? cid=nres142p2_053951). Great differences in soil properties can occur within short distances. Some soils are seasonally wet or subject to flooding. Some are too unstable to be used as a foundation for buildings or roads. Clayey or wet soils are poorly suited to use as septic tank absorption fields. A high water table makes a soil poorly suited to basements or underground installations. The National Cooperative Soil Survey is a joint effort of the United States Department of Agriculture and other Federal agencies, State agencies including the Agricultural Experiment Stations, and local agencies. The Natural Resources Conservation Service (NRCS) has leadership for the Federal part of the National Cooperative Soil Survey. Information about soils is updated periodically. Updated information is available through the NRCS Web Soil Survey, the site for official soil survey information. The U.S. Department of Agriculture (USDA) prohibits discrimination in all its programs and activities on the basis of race, color, national origin, age, disability, and where applicable, sex, marital status, familial status, parental status, religion, sexual orientation, genetic information, political beliefs, reprisal, or because all or a part of an individual's income is derived from any public assistance program. (Not all prohibited bases apply to all programs.) Persons with disabilities who require 2 alternative means for communication of program information (Braille, large print, audiotape, etc.) should contact USDA's TARGET Center at (202) 720-2600 (voice and TDD). To file a complaint of discrimination, write to USDA, Director, Office of Civil Rights, 1400 Independence Avenue, S.W., Washington, D.C. 20250-9410 or call (800) 795-3272 (voice)or(202) 720-6382 (TDD). USDA is an equal opportunity provider and employer. 3 Contents Preface....................................................................................................................2 How Soil Surveys Are Made..................................................................................5 SoilMap.................................................................................................................. 8 SoilMap................................................................................................................9 Legend................................................................................................................10 MapUnit Legend................................................................................................ 11 MapUnit Descriptions.........................................................................................11 Saratoga County, New York............................................................................13 BmB—Bernardston silt loam, 3 to 8 percent slopes....................................13 BmC—Bernardston silt loam, 8 to 15 percent slopes..................................14 BmD—Bernardston silt loam, 15 to 25 percent slopes................................15 PwB—Pittstown silt loam, 3 to 8 percent slopes......................................... 16 References............................................................................................................18 4 How Soil Surveys Are Made Soil surveys are made to provide information about the soils and miscellaneous areas in a specific area. They include a description of the soils and miscellaneous areas and their location on the landscape and tables that show soil properties and limitations affecting various uses. Soil scientists observed the steepness, length, and shape of the slopes; the general pattern of drainage; the kinds of crops and native plants; and the kinds of bedrock. They observed and described many soil profiles. A soil profile is the sequence of natural layers, or horizons, in a soil. The profile extends from the surface down into the unconsolidated material in which the soil formed or from the surface down to bedrock. The unconsolidated material is devoid of roots and other living organisms and has not been changed by other biological activity. Currently, soils are mapped according to the boundaries of major land resource areas (MLRAs). MLRAs are geographically associated land resource units that share common characteristics related to physiography, geology, climate, water resources, soils, biological resources, and land uses (USDA, 2006). Soil survey areas typically consist of parts of one or more MLRA. The soils and miscellaneous areas in a survey area occur in an orderly pattern that is related to the geology, landforms, relief, climate, and natural vegetation of the area. Each kind of soil and miscellaneous area is associated with a particular kind of landform or with a segment of the landform. By observing the soils and miscellaneous areas in the survey area and relating their position to specific segments of the landform, a soil scientist develops a concept, or model, of how they were formed. Thus, during mapping, this model enables the soil scientist to predict with a considerable degree of accuracy the kind of soil or miscellaneous area at a specific location on the landscape. Commonly, individual soils on the landscape merge into one another as their characteristics gradually change. To construct an accurate soil map, however, soil scientists must determine the boundaries between the soils. They can observe only a limited number of soil profiles. Nevertheless, these observations, supplemented by an understanding of the soil-vegetation-landscape relationship, are sufficient to verify predictions of the kinds of soil in an area and to determine the boundaries. Soil scientists recorded the characteristics of the soil profiles that they studied. They noted soil color, texture, size and shape of soil aggregates, kind and amount of rock fragments, distribution of plant roots, reaction, and other features that enable them to identify soils. After describing the soils in the survey area and determining their properties, the soil scientists assigned the soils to taxonomic classes (units). Taxonomic classes are concepts. Each taxonomic class has a set of soil characteristics with precisely defined limits. The classes are used as a basis for comparison to classify soils systematically. Soil taxonomy, the system of taxonomic classification used in the United States, is based mainly on the kind and character of soil properties and the arrangement of horizons within the profile. After the soil 5 Custom Soil Resource Report scientists classified and named the soils in the survey area, they compared the individual soils with similar soils in the same taxonomic class in other areas so that they could confirm data and assemble additional data based on experience and research. The objective of soil mapping is not to delineate pure map unit components; the objective is to separate the landscape into landforms or landform segments that have similar use and management requirements. Each map unit is defined by a unique combination of soil components and/or miscellaneous areas in predictable proportions. Some components may be highly contrasting to the other components of the map unit. The presence of minor components in a map unit in no way diminishes the usefulness or accuracy of the data. The delineation of such landforms and landform segments on the map provides sufficient information for the development of resource plans. If intensive use of small areas is planned, onsite investigation is needed to define and locate the soils and miscellaneous areas. Soil scientists make many field observations in the process of producing a soil map. The frequency of observation is dependent upon several factors, including scale of mapping, intensity of mapping, design of map units, complexity of the landscape, and experience of the soil scientist. Observations are made to test and refine the soil-landscape model and predictions and to verify the classification of the soils at specific locations. Once the soil-landscape model is refined, a significantly smaller number of measurements of individual soil properties are made and recorded. These measurements may include field measurements, such as those for color, depth to bedrock, and texture, and laboratory measurements, such as those for content of sand, silt, clay, salt, and other components. Properties of each soil typically vary from one point to another across the landscape. Observations for map unit components are aggregated to develop ranges of characteristics for the components. The aggregated values are presented. Direct measurements do not exist for every property presented for every map unit component. Values for some properties are estimated from combinations of other properties. While a soil survey is in progress, samples of some of the soils in the area generally are collected for laboratory analyses and for engineering tests. Soil scientists interpret the data from these analyses and tests as well as the field-observed characteristics and the soil properties to determine the expected behavior of the soils under different uses. Interpretations for all of the soils are field tested through observation of the soils in different uses and under different levels of management. Some interpretations are modified to fit local conditions, and some new interpretations are developed to meet local needs. Data are assembled from other sources, such as research information, production records, and field experience of specialists. For example, data on crop yields under defined levels of management are assembled from farm records and from field or plot experiments on the same kinds of soil. Predictions about soil behavior are based not only on soil properties but also on such variables as climate and biological activity. Soil conditions are predictable over long periods of time, but they are not predictable from year to year. For example, soil scientists can predict with a fairly high degree of accuracy that a given soil will have a high water table within certain depths in most years, but they cannot predict that a high water table will always be at a specific level in the soil on a specific date. After soil scientists located and identified the significant natural bodies of soil in the survey area, they drew the boundaries of these bodies on aerial photographs and 6 Custom Soil Resource Report identified each as a specific map unit. Aerial photographs show trees, buildings, fields, roads, and rivers, all of which help in locating boundaries accurately. 7 Soil Map The soil map section includes the soil map for the defined area of interest, a list of soil map units on the map and extent of each map unit, and cartographic symbols displayed on the map. Also presented are various metadata about data used to produce the map, and a description of each soil map unit. 8 Custom Soil Resource Report M Soil Map a v v 600830 600880 600930 600980 601030 601080 601130 601180 601230 601280 601330 43°3'17"N 43°317 N v �22 YrS a v cro v _ IT BmD 10 re BmB m co r v v V O it the 43°3W N '' - `[ 43°3 6"N 600830 600880 600930 600980 601030 601080 601130 601180 601230 601280 601330 3 3 c+ Map Scale:1:2,460 W printed on A landscape(11"x 8.5")sheet. Meters N 0 35 70 140 210 rat 0 100 200 400 600 Map projection:Web Mercator Comer coordinates:WGS84 Edge tics:UTM Zone 18N WGS84 9 Custom Soil Resource Report MAP LEGEND MAP INFORMATION Area of Interest(AOI) Spoil Area The soil surveys that comprise your AOI were mapped at 0 Area of Interest(AOI) Stony Spot 1:24,000. Soils Very Stony Spot 0 Soil Map Unit Polygons Warning:Soil Map may not be valid at this scale. Wet Spot P1 0 Soil Map Unit Lines Enlargement of maps beyond the scale of mapping can cause Other misunderstanding of the detail of mapping and accuracy of soil � Soil Map Unit Points 9 pp 9 Y .- Special Line Features line placement.The maps do not show the small areas of Special Point Features contrasting soils that could have been shown at a more detailed Lo Blowout Water Features scale. - Streams and Canals Borrow Pit Transportation Please rely on the bar scale on each map sheet for map Clay Spot 1-44 Rails measurements. Closed Depression Interstate Highways Gravel Pit Source of Map: Natural Resources Conservation Service US Routes Web Soil Survey URL: Gravelly Spot Major Roads Coordinate System: Web Mercator(EPSG:3857) 0 Landfill Local Roads Maps from the Web Soil Survey are based on the Web Mercator Lava Flow Background projection,which preserves direction and shape but distorts distance and area.A projection that preserves area,such as the Marsh or swamp Aerial Photography Albers equal-area conic projection,should be used if more Mine or Quarry accurate calculations of distance or area are required. Miscellaneous Water This product is generated from the USDA-NRCS certified data as Perennial Water of the version date(s)listed below. Rock Outcrop Soil Survey Area: Saratoga County,New York Saline Spot Survey Area Data: Version 23,Sep 6,2023 Sandy Spot Soil map units are labeled(as space allows)for map scales Severely Eroded Spot 1:50,000 or larger. Sinkhole Date(s)aerial images were photographed: Sep 9,2022—Oct 22, Slide or Slip 2022 oa Sodic Spot The orthophoto or other base map on which the soil lines were compiled and digitized probably differs from the background imagery displayed on these maps.As a result,some minor shifting of map unit boundaries may be evident. 10 Custom Soil Resource Report Map Unit Legend Map Unit Symbol Map Unit Name Acres in AOI Percent of AOI BmB Bernardston silt loam,3 to 8 5.5 37.5% percent slopes BmC Bernardston silt loam,8 to 15 2.4 16.5% percent slopes BmD Bernardston silt loam, 15 to 25 5.4 36.7% percent slopes PwB Pittstown silt loam,3 to 8 1.4 9.3% percent slopes Totals for Area of Interest 14.6 100.0% Map Unit Descriptions The map units delineated on the detailed soil maps in a soil survey represent the soils or miscellaneous areas in the survey area. The map unit descriptions, along with the maps, can be used to determine the composition and properties of a unit. A map unit delineation on a soil map represents an area dominated by one or more major kinds of soil or miscellaneous areas. A map unit is identified and named according to the taxonomic classification of the dominant soils. Within a taxonomic class there are precisely defined limits for the properties of the soils. On the landscape, however, the soils are natural phenomena, and they have the characteristic variability of all natural phenomena. Thus, the range of some observed properties may extend beyond the limits defined for a taxonomic class. Areas of soils of a single taxonomic class rarely, if ever, can be mapped without including areas of other taxonomic classes. Consequently, every map unit is made up of the soils or miscellaneous areas for which it is named and some minor components that belong to taxonomic classes other than those of the major soils. Most minor soils have properties similar to those of the dominant soil or soils in the map unit, and thus they do not affect use and management. These are called noncontrasting, or similar, components. They may or may not be mentioned in a particular map unit description. Other minor components, however, have properties and behavioral characteristics divergent enough to affect use or to require different management. These are called contrasting, or dissimilar, components. They generally are in small areas and could not be mapped separately because of the scale used. Some small areas of strongly contrasting soils or miscellaneous areas are identified by a special symbol on the maps. If included in the database for a given area, the contrasting minor components are identified in the map unit descriptions along with some characteristics of each. A few areas of minor components may not have been observed, and consequently they are not mentioned in the descriptions, especially where the pattern was so complex that it was impractical to make enough observations to identify all the soils and miscellaneous areas on the landscape. 11 Custom Soil Resource Report The presence of minor components in a map unit in no way diminishes the usefulness or accuracy of the data. The objective of mapping is not to delineate pure taxonomic classes but rather to separate the landscape into landforms or landform segments that have similar use and management requirements. The delineation of such segments on the map provides sufficient information for the development of resource plans. If intensive use of small areas is planned, however, onsite investigation is needed to define and locate the soils and miscellaneous areas. An identifying symbol precedes the map unit name in the map unit descriptions. Each description includes general facts about the unit and gives important soil properties and qualities. Soils that have profiles that are almost alike make up a soil series. Except for differences in texture of the surface layer, all the soils of a series have major horizons that are similar in composition, thickness, and arrangement. Soils of one series can differ in texture of the surface layer, slope, stoniness, salinity, degree of erosion, and other characteristics that affect their use. On the basis of such differences, a soil series is divided into soil phases. Most of the areas shown on the detailed soil maps are phases of soil series. The name of a soil phase commonly indicates a feature that affects use or management. For example, Alpha silt loam, 0 to 2 percent slopes, is a phase of the Alpha series. Some map units are made up of two or more major soils or miscellaneous areas. These map units are complexes, associations, or undifferentiated groups. A complex consists of two or more soils or miscellaneous areas in such an intricate pattern or in such small areas that they cannot be shown separately on the maps. The pattern and proportion of the soils or miscellaneous areas are somewhat similar in all areas. Alpha-Beta complex, 0 to 6 percent slopes, is an example. An association is made up of two or more geographically associated soils or miscellaneous areas that are shown as one unit on the maps. Because of present or anticipated uses of the map units in the survey area, it was not considered practical or necessary to map the soils or miscellaneous areas separately. The pattern and relative proportion of the soils or miscellaneous areas are somewhat similar. Alpha-Beta association, 0 to 2 percent slopes, is an example. An undifferentiated group is made up of two or more soils or miscellaneous areas that could be mapped individually but are mapped as one unit because similar interpretations can be made for use and management. The pattern and proportion of the soils or miscellaneous areas in a mapped area are not uniform. An area can be made up of only one of the major soils or miscellaneous areas, or it can be made up of all of them. Alpha and Beta soils, 0 to 2 percent slopes, is an example. Some surveys include miscellaneous areas. Such areas have little or no soil material and support little or no vegetation. Rock outcrop is an example. 12 Custom Soil Resource Report Saratoga County, New York BmB—Bernardston silt loam, 3 to 8 percent slopes Map Unit Setting National map unit symbol: 9w8y Elevation: 0 to 1,000 feet Mean annual precipitation: 36 to 48 inches Mean annual air temperature: 45 to 48 degrees F Frost-free period: 125 to 160 days Farmland classification: All areas are prime farmland Map Unit Composition Bernardston and similar soils: 85 percent Minor components: 15 percent Estimates are based on observations, descriptions, and transects of the mapunit. Description of Bernardston Setting Landform:Till plains, hills, drumlinoid ridges Landform position (two-dimensional): Summit Landform position (three-dimensional): Crest Down-slope shape: Convex Across-slope shape: Convex Parent material: Loamy, acid, dense till derived mainly from phyllite, shale, slate, and schist Typical profile H1 - 0 to 10 inches: silt loam H2- 10 to 26 inches: channery loam H3- 26 to 72 inches: channery silt loam Properties and qualities Slope: 3 to 8 percent Depth to restrictive feature: 20 to 30 inches to densic material Drainage class:Well drained Capacity of the most limiting layer to transmit water(Ksat): Moderately low to moderately high (0.06 to 0.20 in/hr) Depth to water table:About 18 to 24 inches Frequency of flooding: None Frequency of ponding: None Available water supply, 0 to 60 inches: Low(about 4.6 inches) Interpretive groups Land capability classification (irrigated): None specified Land capability classification (nonirrigated): 2e Hydrologic Soil Group: C/D Ecological site: F144AY007CT-Well Drained Dense Till Uplands Hydric soil rating: No Minor Components Pittstown Percent of map unit: 10 percent Hydric soil rating: No 13 Custom Soil Resource Report Manlius Percent of map unit: 5 percent Hydric soil rating: No BmC—Bernardston silt loam, 8 to 15 percent slopes Map Unit Setting National map unit symbol: 9w8z Elevation: 0 to 1,000 feet Mean annual precipitation: 36 to 48 inches Mean annual air temperature: 45 to 48 degrees F Frost-free period: 125 to 160 days Farmland classification: Farmland of statewide importance Map Unit Composition Bernardston and similar soils: 85 percent Minor components: 15 percent Estimates are based on observations, descriptions, and transects of the mapunit. Description of Bernardston Setting Landform:Till plains, hills, drumlinoid ridges Landform position (two-dimensional): Shoulder Landform position (three-dimensional): Crest Down-slope shape: Convex Across-slope shape: Convex Parent material: Loamy, acid, dense till derived mainly from phyllite, shale, slate, and schist Typical profile H1 - 0 to 10 inches: silt loam H2- 10 to 26 inches: channery loam H3- 26 to 72 inches: channery silt loam Properties and qualities Slope: 8 to 15 percent Depth to restrictive feature: 20 to 30 inches to densic material Drainage class:Well drained Capacity of the most limiting layer to transmit water(Ksat): Moderately low to moderately high (0.06 to 0.20 in/hr) Depth to water table:About 18 to 24 inches Frequency of flooding: None Frequency of ponding: None Available water supply, 0 to 60 inches: Low(about 4.6 inches) Interpretive groups Land capability classification (irrigated): None specified Land capability classification (nonirrigated): 3e Hydrologic Soil Group: C/D 14 Custom Soil Resource Report Ecological site: F144AY007CT-Well Drained Dense Till Uplands Hydric soil rating: No Minor Components Pittstown Percent of map unit: 10 percent Hydric soil rating: No Manlius Percent of map unit: 5 percent Hydric soil rating: No BmD—Bernardston silt loam, 15 to 25 percent slopes Map Unit Setting National map unit symbol: 9w90 Elevation: 0 to 1,000 feet Mean annual precipitation: 36 to 48 inches Mean annual air temperature: 45 to 48 degrees F Frost-free period: 125 to 160 days Farmland classification: Not prime farmland Map Unit Composition Bernardston and similar soils: 85 percent Minor components: 15 percent Estimates are based on observations, descriptions, and transects of the mapunit. Description of Bernardston Setting Landform:Till plains, hills, drumlinoid ridges Landform position (two-dimensional): Backslope Landform position (three-dimensional): Side slope Down-slope shape: Convex Across-slope shape: Convex Parent material: Loamy, acid, dense till derived mainly from phyllite, shale, slate, and schist Typical profile H1 - 0 to 10 inches: silt loam H2- 10 to 26 inches: channery loam H3- 26 to 72 inches: channery silt loam Properties and qualities Slope: 15 to 25 percent Depth to restrictive feature: 20 to 30 inches to densic material Drainage class:Well drained Capacity of the most limiting layer to transmit water(Ksat): Moderately low to moderately high (0.06 to 0.20 in/hr) Depth to water table:About 18 to 24 inches 15 Custom Soil Resource Report Frequency of flooding: None Frequency of ponding: None Available water supply, 0 to 60 inches: Low (about 4.6 inches) Interpretive groups Land capability classification (irrigated): None specified Land capability classification (nonirrigated): 4e Hydrologic Soil Group: C/D Ecological site: F144AY007CT-Well Drained Dense Till Uplands Hydric soil rating: No Minor Components Pittstown Percent of map unit: 10 percent Hydric soil rating: No Manlius Percent of map unit: 5 percent Hydric soil rating: No PwB—Pittstown silt loam, 3 to 8 percent slopes Map Unit Setting National map unit symbol: 9wcc Elevation: 200 to 520 feet Mean annual precipitation: 36 to 48 inches Mean annual air temperature: 45 to 48 degrees F Frost-free period: 125 to 160 days Farmland classification: All areas are prime farmland Map Unit Composition Pittstown and similar soils: 80 percent Minor components: 20 percent Estimates are based on observations, descriptions, and transects of the mapunit. Description of Pittstown Setting Landform:Till plains, hills, drumlinoid ridges Landform position (two-dimensional): Summit Landform position (three-dimensional): Crest Down-slope shape: Concave Across-slope shape: Convex Parent material: Loamy till Typical profile H1 - 0 to 11 inches: silt loam H2- 11 to 23 inches: gravelly loam H3- 23 to 72 inches: gravelly loam 16 Custom Soil Resource Report Properties and qualities Slope: 3 to 8 percent Depth to restrictive feature: 15 to 30 inches to densic material Drainage class: Moderately well drained Capacity of the most limiting layer to transmit water(Ksat): Moderately low to moderately high (0.06 to 0.57 in/hr) Depth to water table:About 18 to 30 inches Frequency of flooding: None Frequency of ponding: None Available water supply, 0 to 60 inches: Low (about 4.1 inches) Interpretive groups Land capability classification (irrigated): None specified Land capability classification (nonirrigated): 2e Hydrologic Soil Group: C/D Ecological site: F144AY037MA- Moist Dense Till Uplands Hydric soil rating: No Minor Components Bernardston Percent of map unit. 10 percent Hydric soil rating: No Manlius Percent of map unit. 10 percent Hydric soil rating: No 17 References American Association of State Highway and Transportation Officials (AASHTO). 2004. Standard specifications for transportation materials and methods of sampling and testing. 24th edition. American Society for Testing and Materials (ASTM). 2005. Standard classification of soils for engineering purposes. ASTM Standard D2487-00. Cowardin, L.M., V. Carter, F.C. Golet, and E.T. LaRoe. 1979. Classification of wetlands and deep-water habitats of the United States. U.S. Fish and Wildlife Service FWS/OBS-79/31. Federal Register. July 13, 1994. Changes in hydric soils of the United States. Federal Register. September 18, 2002. Hydric soils of the United States. Hurt, G.W., and L.M. Vasilas, editors. Version 6.0, 2006. Field indicators of hydric soils in the United States. National Research Council. 1995. Wetlands: Characteristics and boundaries. Soil Survey Division Staff. 1993. Soil survey manual. Soil Conservation Service. U.S. Department of Agriculture Handbook 18. http://www.nres.usda.gov/wps/portal/ nres/detail/national/soils/?cid=nres 142p2_054262 Soil Survey Staff. 1999. Soil taxonomy: A basic system of soil classification for making and interpreting soil surveys. 2nd edition. Natural Resources Conservation Service, U.S. Department of Agriculture Handbook 436. http:// www.nres.usda.gov/wps/portal/nres/detail/national/soils/?cid=nres142p2_053577 Soil Survey Staff. 2010. Keys to soil taxonomy. 11th edition. U.S. Department of Agriculture, Natural Resources Conservation Service. http:// www.nres.usda.gov/wps/portal/nres/detail/national/soils/?cid=nres142p2_053580 Tiner, R.W., Jr. 1985. Wetlands of Delaware. U.S. Fish and Wildlife Service and Delaware Department of Natural Resources and Environmental Control, Wetlands Section. United States Army Corps of Engineers, Environmental Laboratory. 1987. Corps of Engineers wetlands delineation manual. Waterways Experiment Station Technical Report Y-87-1. United States Department of Agriculture, Natural Resources Conservation Service. National forestry manual. http://www.nres.usda.gov/wps/portal/nres/detail/soils/ home/?cid=nres142p2_053374 United States Department of Agriculture, Natural Resources Conservation Service. National range and pasture handbook. http://www.nres.usda.gov/wps/portal/nres/ detail/national/landuse/rangepasture/?cid=stelprdb1043084 18 Custom Soil Resource Report United States Department of Agriculture, Natural Resources Conservation Service. National soil survey handbook, title 430-VI. http://www.nres.usda.gov/wps/portal/ nres/detail/soils/scientists/?cid=nres142p2_054242 United States Department of Agriculture, Natural Resources Conservation Service. 2006. Land resource regions and major land resource areas of the United States, the Caribbean, and the Pacific Basin. U.S. Department of Agriculture Handbook 296. http://www.nres.usda.gov/wps/portal/nres/detail/national/soils/? cid=nres142p2_053624 United States Department of Agriculture, Soil Conservation Service. 1961. Land capability classification. U.S. Department of Agriculture Handbook 210. http:// www.nrcs.usda.gov/lnternet/FSE—DOCUMENTS/nrcsl 42p2_052290.pdf 19 APPENDIX C EROSION AND SEDIMENT CONTROL DRAWINGS stud *ioA LANDSCAPE ARCHITECTURE I ENGINEERING I PLANNING 5/IR. TRUST I QUALITY COLLABORATION I INNOVATION WOOD) / 5/811IR. 94 I / r 19 4- 74 Warren Street, Suite 1 Saratoga Springs, NY 12866 518.450.4030 LEGEND /� ow ° ,10'E 255 / `�Oy ��j` PROPERTY LINE / / w N� — g8�3�/ W0098' /ry A20��>o LIMITS OF DISTURBANCE # / / ,� / 060�(O —SF —SF — SILT FENCE P a6o EXISTING MAJOR CONTOURS Z v� w/w / ,� 0 w/ / / / / ,O� J S / EXISTING MINOR CONTOURS WOODGfe -7 v WETLANDS w 1 / / / / / (� ( EXISTING SURFACE 6 / /�Z N T/ \ 0 BE REMOVED # w E ` / / / 1 5 8'IR. # w 0°0300 / / \ / TREES TO BE CLEARED / STABILIZED CONSTRUCTION z � w�j ENTRANCE w NORTH o �W N89 2� � / 0 5/8"IR. GRAPHIC SCALE \ �NOODS / / / / I 50 0 25 50 100 4/// I INCH = 50 FEET LOCATION OF MUNICIPAL WATER MAIN / / / 1` Q� � l l ON 24 X 36 SHEET N \ 7(,c))6 C/4, BASE MAP INFORMATION OBTAINED FROM "MAP OF LANDS OF FRANK SCARPINATO AND DIANE RADEMACHER - ( 76' SCARPINATO, SITUATE AT 247 KAYDEROSS AVENUE EAST, CITY OF SARATOGA SPRINGS, SARATOGA COUNTY, NY,' DATED NOVEMBER 10, 2023 BY THOMPSON FLEMING LAND ,av \ — — ► — — — _ / / / SURVEYORS, P.C. - - _ r_ - - � 2 � � ♦ ♦ GREENHOUSE — � DIG SAFE NOTE: SILT FENCE (TYP ) THIS PLAN SET WAS DRAFTED WITHOUT THE BENEFIT OF . ♦ / "DIG SAFE" MARKINGS. UTILITIES SHOWN ARE NOT 1 L-5.10/ / J \ ( REPAIR PORTION OF EXISTING DRIVEWAY AS REQ'D WARRANTED TO BE EXACT OR COMPLETE. THE CONTRACTOR SHALL CONTACT "DIG SAFE" AT 811 BEFORE COMMENCING ANY WORK AND SHALL PRESERVE EXISTING / ` ♦ UTILITIES WHICH ARE NOT SPECIFIED TO BE REMOVED IN THIS PLAN SET. 0 1 / EXISTING GREENHOUSE 5/g" s `37p�\ l REVISIONS SF TO BE RELOCATED / Area= o � 33�\ DATE DESCRIPTION / 1 3.369 (6C` 4/4/24 SUBDIVISION REVIEW / CONCRETE WASHOUT AREA L-5.10 0.155 AC. AREA TO OF TREES TO BE CLEARED 1 I ' / /� �3�, , / FOR POTABLE WATER SERVICE CONNECTION ` ` ` 1/ SILT FENCE (TYP.) L-5.10 \ 3�560 ` V 70 CIO v l C, It / / v / / / /� / ` / TOPSOIL STOCK PILE 2 4 / / � � IT IS A VIOLATION OF NEW PORK STATE EDUCATION LAW FOR ANY PERSON, � UNLESS THEY ARE ACTING UNDER THE DIRECTION OF A LICENSED 0 " PROFESSIONAL ENGINEER, ARCHITECT, LANDSCAPE ARCHITECT, OR LAND 2 2 / SURROUNDED BY SILT FENCE L-5.10 L-5.10 0 5/8" 2, S33°02 23 W L-5.10 SILT FENCE (TYP.) / / \ /� SURVEYOR, TO ALTER ANY ITEM IN ANY WAY. IF AN ITEM BEARING THE STAMP ° OF A LICENSED PROFESSIONAL IS ALTERED, THE ALTERING LICENSED 55.00 PROFESSIONAL SHALL STAMP THE DOCUMENT AND INCLUDE THE NOTATION "ALTERED BY' FOLLOWED BY THEIR SIGNATURE, THE DATE OF SUCH mo / / SF / / / 3 STABILIZED CONSTRUCTION ENTRANCE / ALTERNATION,AND SPECIFIC DESCRIPTION of THE ALTERATION. z /�- 2�� L-5.10 SILT FENCE (TYP.) Q) DRAWINGS 1 / a EXISTING TREE LINE TO REMAIN NOT FO R CONSTRUCTION 2 SILT FENCE (TYP.) L-5.10 / / / ♦ _ 2 L-5.10 SILT FENCE (TYP.) CONCRETE WASHOUT AREA PREPARED FOR I — � FRANK SCARPINATO 247 KAYDEROSS AVENUE EAST 0 SARATOGA SPRINGS, NY 12866 LIMITS OF DISTURBANCE ±2.546AC. / �- �/ � WOODS - / o I / l 5/8'IR. PROJECT 1 _ _ \ KAYDEROSS SPRINGS r 0.021 AC. AREA TO OF TREES TO I Ipw 612.46 )��el oprn en t, I n> � CONSERVATION BE CLEARED FOR ADJACENT \ PARCEL ACCESS IN FUTURE — N83°40 02 / Riley Fa #20220103701 SUBDIVISION 5/8"IRo� GNP , DRAWING TITLE Q N DEMOLITION, EROSION , & Quo n1f =� w Fad SEDIMENT CONTROL PLAN s N Riley t, Inc. rRil Riley Farm PROJECT NO. 21008 ww DATE: DRAWING NO. L<z 4/4/2024 L_O . 30 ww Q J a cn� DWG 4 OF 10