Harbor View Forest Stand Delineation and Natural Resource Inventory by Rick Hammond

SUBMITTED TO:

The Maryland-National Capital Park and Planning Commission Prince Georgeâ&#x20AC;&#x2122;s County Planning Department

HARBOR VIEW FOREST STAND DELINEATION November 2018

Environmental Planning Section 14741 Governor Oden Bowie Drive Upper Marlboro, Maryland 20772

Prepared By:

Richard Hammond and Robert Boyd (CV Inc)

Forest Stand Delineation Harbor View November 2018

TABLE OF CONTENTS SUMMARY

SITE LOCATION

EXISTING ENVIRONMENTAL CONDITIONS

Soils

Rare, Threatened, and Endangered Species

Land Use

Hydrology and Wetlands

FOREST STAND DELINEATION METHODOLOGY

FOREST STAND DESCRIPTION

Forest Stand A

Forest Stand B

SPECIMEN TREES

CONCLUSIONS

REFERENCES

APPENDIX A – SITE MAPS APPENDIX B – SOIL REPORT APPENDIX C – FOREST STAND DATA AND STRUCTURE ANALYSIS SHEETS APPENDIX D – AGENCY CORRESPONDENCE APPENDIX E – QUALIFICATIONS APPENDIX F – PHOTOGRAPHIC DOCUMENTATION APPENDIX G – NATURAL RESOURCE INVENTORY 2

Forest Stand Delineation Harbor View November 2018

FOREST STAND DELINEATION REPORT SUMMARY The Maryland Forest Conservation Act of 1991 was created to protect the remaining forests within the state of Maryland in order to maintain the quality of life for its residents. The first step in preservation is taking an inventory of existing site conditions by conducting a Forest Stand Delineation (FSD). These delineations determine the most suitable and practical areas for conservation of forest resources during the development review process (Natural Resource Article 5-1604 of the FCA, 1991). FSDs are preformed by a Qualified Professional to the standards required by state and local statutes. This FSD was completed in November 2018, in compliance with the Prince George’s County Environmental Technical Manual (September 2010). Field work was performed by Richard Hammond and Robert Boyd on November 8th, 2018. The procedures used in this FSD satisfy the requirements of the Prince George’s County Environmental Technical Manual, as administered by the Maryland-National Capital Park and Planning Commission, Prince George’s County Planning Department. Procedures outlined in the Prince George’s County Environmental Technical Manual were used to define sampling methods and strategies. The Harbor View site is approximately 4.69 acres in size and is zoned for Residential use (Zoning category R-R). The field investigation resulted in the delineation of 4.69 acres of forested land on the property. The forested portion of the stand is delineated into two (2) forest stands: Stand A – Mature Oak and Stand B – Mature Oak – Beech. Nine (9) specimen trees were delineated on site. The specimen trees are in Good to Fair condition and are listed on page seven (7). No rare, threatened, or endangered species were found during the field review. This narrative includes a description of each stand, documentation of vegetation on-site, site geography and physiography, stand data sheets, and a completed FSD Checklist.

SITE LOCATION The project site is located on a tract of land on Fort Washington Road, adjacent to a property marked as 11911 Fort Washington Road, Fort Washington, MD 20744 Prince George’s County. The project area consists entirely of mixed-forest, bordered by residential areas on the North, South, and West, and by Fort Washington Road to the East. Table 1 summarizes accompanying location and acreage data for the site.

Forest Stand Delineation Harbor View November 2018 TABLE 1: LOCATION DATA FOR FSD PROJECT AREA Site Address Fort Washington Road, Fort Washington, MD 20744 GPS Location (Lat, Long) 38.7307, -77.0050 ADC Map 45J4 - 45K4 Map 5880 Total Tract Acreage 4.69 Total Forested Acreage 4.69 Physiographic province Atlantic Coastal Plain Land Resource Region Northern Atlantic Slope Diversified Farming Region (LRR S) Major Land Resource Area Northern Coastal Plain (149A) Watershed Middle Potomac (DNR #021402010794)

EXISTING ENVIRONMENTAL CONDITIONS Topography on site varies in elevation from 69 feet above mean sea level (AMSL) to 58 feet ASML at the lowest point. There are no regulated water resources present on or adjacent to the subject area. Inspection of the Federal Emergency Management Agencyâ&#x20AC;&#x2122;s (FEMA) Flood Insurance Rate Map for this location determined there are no mapped FEMA 100-year floodplain areas on this property. A floodplain delineation preformed by Prince Georgeâ&#x20AC;&#x2122;s County Department of Permitting, Inspections, and Enforcement (DPIE) confirmed that there are no floodplains on this property. Soils According to the NRCS Web Soil Survey, three (3) soil types are present on the subject property. The following table lists the soil symbols, soil names, K-factors, hydrologic soil groups, drainage classes, and hydric rating of the soils on-site. TABLE 2: SOIL INFORMATION Hydrologic Symbol Name K-Factor Soil Group Piccowaxen - Liverpool complex, PoA 0 to 2 percent slopes 0.37 C/D Liverpool - Piccowaxen complex, LxD 5 to 15 percent slopes 0.43 D Piccowaxen - Urban land PrB complex, 0 to 5 percent slopes 0.37 C/D

Drainage Class Somewhat Poorly Drained Moderatley Well Drained Somewhat Poorly Drained

Hydric Rating Not Hydric Not Hydric Not Hydric

Rare, Threatened, and Endangered Species The Maryland Department of Natural Resources Natural Heritage Program was contacted to determine if the presence of rare, threatened, or endangered species has been reported on the site (Appendix D). Documentation has not been received to date from the Program; however, according to the GIS layer, the property is not located within a Sensitive Species Project Review Area. Land Use The Harbor View property is an undeveloped property that consists entirely of forested land. The property is bound by residential properties to the North, South, East, and West. Fort Washington Road runs along the Eastern Boundary of the site. There is encroachment from Lot 7 and Lot 8 on the 4

Forest Stand Delineation Harbor View November 2018 northern border of the site. The Prince George’s County Historic Preservation Division and the Maryland Historical Trust were both contacted. The Prince George’s County Historic Preservation Division responded back by phone on November 19th, 2018 at 3:00 PM to state that “there are no recorded historical features on the site”. A response from The Maryland Historical Trust has not been received to date. Hydrology and Wetlands An in-office review of U.S. Fish and Wildlife National Wetland Inventory maps, Maryland Department of Natural Resources Wetland Maps, the NRCS Web Soil Survey, and the USGS 7.5 Minute Quadrangle for Fort Washington, Maryland were reviewed to identify potential areas within the study that had a strong probability of being wetlands. A review of these maps did not indicate that wetlands may exist on the Harbor View Property. After field work was conducted, no hydric soils were found on site and hydrophytic indicator species were not present. Saturated areas were present; however, a heavy rain event had occurred two days prior to field work. Man-made drainage channels and sediment control facilities were present on the site boundaries. Robert Boyd, PLA AICP, determined that these areas did not meet wetland qualifications.

FOREST STAND DELINEATION METHODOLOGY Prior to conducting the FSD, aerial photographs, environmental, and topographic maps were reviewed to determine possible stand boundaries, anthropogenic and environmental (i.e. wetlands, streams, etc.) features, and a sampling strategy for the site. The Prince George’s County Environmental Technical Manual requires a minimum of one (1) 1/10-acre plot per four (4) acres of forest stand area, a minimum of two (2) plots per forest stand, and a minimum of three (3) plots for the total forested area. A total of four (4) plots were pre-selected by random generation. Pre-selected points were adjusted in the field to ensure representative sampling of all forest stands on site. A 10-factor tree gauge was used to calculate the basal area of trees in each plot and the overall forest stand density. Diameter tape was used to determine the diameter at breast height (DBH) of trees. The FSD also determined the percent of canopy, understory, herbaceous, and invasive species cover at each sample plot. Any specimen trees 1 were identified and asses for their overall condition (Poor, Fair, Good, Excellent) 2 with their locations marked on the NRI plan. The information collected in the field was used to determine successional stage and assign a forest structure value 3 for each stand to aid in evaluating the overall value, health, and retention of each stand.

1 A specimen tree is defined as a tree with a diameter-at-breast height (DBH) of 30 inches or greater; trees having 75% or more of the DBH of the current champion of that species; or a particularly impressive or unusual example of a species due to its size, shape, age, or any other trait that epitomizes the character of the species (M-NCPPC, 2010). Sizes and locations of MD county champion trees can be found at http://mdbigtrees.com/ 2 Tree condition was assessed using the Maryland-National Capital Park and Planning Commission’s (M-NCPPC) Environmental Technical Manual for Prince George’s County, Maryland (M-NCPPC, 2010, Appendix A – 12) 3 Forest structure value was assessed for each stand using the Maryland – National Capitol Park and Planning Commission’s (M-NCPPC) “Environmental Technical Manual” for Prince George’s County, Maryland (M-NCPPC, 2010, Forest Stand Structure Analysis Form, Appendix A – 1)

Forest Stand Delineation Harbor View November 2018

FOREST STAND DESCRIPTION Stand A (Mature Oak) Forest Stand A encompasses approximately 125,888 square feet (2.89 acres) of the property and consists of mature mixed oak trees (Quercus spp.). The stand is located on the eastern portion of the property. The forest stand has a ‘Medium’ priority for preservation. The forest stand has an estimated density of 120 trees/ac and a basal area of 135 sf/ac. Approximately <5% of the stand consists of observed invasive species, however as field work was conducted in early November this may be higher in other parts of the year. The dominant canopy structure of Forest Stand A consists of Oak (Quercus alba, Quercus rubra). Other species present within the canopy consist of Pignut Hickory (Carya glabra), Red Maple (Acer rubrum), Swamp White Oak (Quercus bicolor), and American Elm (Ulmus americana). Common understory species include American Holly (Ilex opaca), American Beech (Fagus grandifolia), Pignut Hickory, Sweetgum (Liquidamber styraciflua) and Green Briar (Smilax rotundifolia). Herbaceous species include Sweetgum, Red Oak, Willow Oak (Quercus phellos) and Carex spp. While not noted within plot areas, Japanese Stilt Grass (Microstegium vimineum) was observed within the stand. Stand B (Mature Oak-Beech) Forest Stand B encompasses approximately 78,408 square feet (1.80 acres) of the property and consists of mature mixed oak trees (Quercus spp.) and American beech (Fagus grandifolia). The stand is located on the eastern portion of the property. The forest stand has a ‘Medium’ priority for preservation. The forest stand has an estimated density of 150 trees/ac and a basal area of 130 sf/ac. Approximately <5% of the stand consists of observed invasive species, however as field work was conducted in early November this may be higher in other parts of the year. The dominant canopy structure of Forest Stand B consists of Oak and American Beech. Other species present within the canopy consist of Red Maple, Willow Oak, and Pignut Hickory. Common understory species include American Beech, Pignut Hickory, Red Maple, Paw Paw (Asimina triloba), Wild Azalea (Rhododendren canescens), and High Bush Blueberry (Vaccinium corymbosum). Herbaceous species include White Oak, American Holly, Red Oak, Wild Azalea, and Greenbriar.

SPECIMEN TREES All specimen trees identified on the site property are described in Table 2. The location of each tree is demarcated on the NRI Plan.

Forest Stand Delineation Harbor View November 2018 Tree #

Common Name

TABLE 3: SPECIMEN TREES Botanical Name DBH (in)

Condition*

Comments Heavy lean and a few dead leaders and branches

Red Oak

Quercus rubra

Fair

2 3 4 5

White Oak Red Oak White Oak White Oak

Quercus alba Quercus rubra Quercus alba Quercus alba

30 32 33 39

Good Good Good Good

White Oak

Quercus alba

Fair

Trunk Split at 6 feet height.

7 Southern Red Oak Quercus falcata 30 Good 8 White Oak Quercus alba 38 Good 9 Bur Oak Quercus macrocarpa 30 Good *Tree Condition was assesed using the Maryland-National capital Park and Planning Commision's (M-NCPPC) Environmental Technical Manual for Prince George's County, Maryland (M-NCPPC, 2010, pg A-12)

CONCLUSIONS The property is divided into two (2) stands. Stand A is a Mid Successional Mature Mixed Oak stand with a ‘Medium’ priority for preservation and a ‘Low’ priority for restoration, while Stand B is a Mid Successional Mature Mixed Oak – Beech stand with a ‘Medium’ priority for preservation and a ‘Low’ priority for restoration. The herbaceous layer and invasive species cover were both low and this could be attributed to the time of year that field work was conducted (Early November). The property consists of nine (9) specimen trees, the majority of which are in good condition. It should also be noted that there are a handful of larger trees that did not fall within plot points, but were observed on site. There were also areas of Japanese Stilt Grass that also did not fall within plot points but were observed on site. No wetlands or waters of the U.S. were found on site.

Forest Stand Delineation Harbor View November 2018

REFERENCES Ericson, Tod, Howell, Ginger Page. 1997. State Forest Conservation Technical Manual. Maryland Department of Natural Resources. Annapolis, Maryland. Prince George’s County Staff, 2010. Environmental Technical Manual. Prince George’s County Department of Planning and Zoning. Upper Marlboro, Maryland. NRCS Staff. USDA – Natural Resources Conservation Service, United States Department of Agriculture. Plants Database. Available online at http://plants.usda.gov. Soil Survey Staff. Natural Resources Conservation Service, United States Department of Agriculture. Web Soil Survey. Available online at http://websoilsurvey.nrcs.usda.gov/ . U.S. Fish & Wildlife Staff. U.S. Fish and Wildlife – National Wetlands Inventory. Wetlands Mapper. Available online at http://www.fws.gov/wetlands/data/mapper.html. USGS Staff. U.S. Department of the Interior, U.S. Geologic Survey. USGS Topo Quadrangles – Maps for America. Available online at http://nationalmap.gov/ustopo/index.html Prince George’s County GIS Department. PG ATLAS. Prince George’s County Department of Planning and Zoning, M-NCPPC. Upper Marlboro, Maryland.

APPENDIX A SITE MAPS

Harbor View Vicinity Map Prince George's County, Maryland November 2018

Data Sources:

Project Information: Located adjacent to 11911 Fort Washington Road, Fort Washington MD

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USGS Topo Map

Harbor View

Site Location

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0.5 mi U.S. Fish and Wildlife Service, National Standards and Support Team, wetlands_team@fws.gov

0.7 km

November 9, 2018 Wetlands

Freshwater Emergent Wetland

Lake

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This map is for general reference only. The US Fish and Wildlife Service is not responsible for the accuracy or currentness of the base data shown on this map. All wetlands related data should be used in accordance with the layer metadata found on the Wetlands Mapper web site.

National Wetlands Inventory (NWI) This page was produced by the NWI mapper

National Wetlands Inventory Map Prince George's County, Maryland November 2018

Data Sources:

Project Information: Located adjacent to 11911 For t W ashington Road, For t W ashington MD

Site Location

U.S. Fish and Wildlife Service, National Standards and Support Team, wetlands_team@fws.gov, MD iMAP, DNR, USFW, Sources: Esri, HERE, Garmin, Intermap, increment P Corp., GEBCO, USGS, FAO, NPS, NRCAN, GeoBase, IGN, Kadaster NL, Ordnance Survey, Esri Japan, METI, Esri China (Hong Kong), swisstopo, Â© OpenStreetMap contributors, and the GIS User Community, MD iMAP, MDE, MD iMAP, ESRI

MERLIN Map Prince George's County, Maryland November 2018

Data Sources:

Project Information: Located adjacent to 11911 For t W ashington Road, For t W ashington MD

National Flood Hazard Layer FIRMette

Legend

38°44'1.99"N

77°0'35.75"W

SEE FIS REPORT FOR DETAILED LEGEND AND INDEX MAP FOR FIRM PANEL LAYOUT

Without Base Flood Elevation (BFE) Zone A, V, A99

With BFE or Depth Zone AE, AO, AH, VE, AR

SPECIAL FLOOD HAZARD AREAS

Regulatory Floodway 0.2% Annual Chance Flood Hazard, Areas of 1% annual chance flood with average depth less than one foot or with drainage areas of less than one square mile Zone X Future Conditions 1% Annual Chance Flood Hazard Zone X Area with Reduced Flood Risk due to Levee. See Notes. Zone X Area with Flood Risk due to Levee Zone D

OTHER AREAS OF FLOOD HAZARD NO SCREEN

Area of Minimal Flood Hazard

Zone X

Effective LOMRs

OTHER AREAS

Area of Undetermined Flood Hazard

Zone D

Channel, Culvert, or Storm Sewer Levee, Dike, or Floodwall

GENERAL STRUCTURES B

20.2 17.5

Cross Sections with 1% Annual Chance Water Surface Elevation Coastal Transect Base Flood Elevation Line (BFE) Limit of Study Jurisdiction Boundary Coastal Transect Baseline Profile Baseline Hydrographic Feature

OTHER FEATURES

Digital Data Available No Digital Data Available

MAP PANELS

Unmapped

The pin displayed on the map is an approximate point selected by the user and does not represent an authoritative property location. This map complies with FEMA's standards for the use of digital flood maps if it is not void as described below. The basemap shown complies with FEMA's basemap accuracy standards

250

500

1,000

1,500

Feet 2,000

1:6,000

Data Sources: Prince George's County, Maryland November 2018

38°43'33.92"N

76°59'58.29"W

USGS The National Map: Orthoimagery. Data refreshed October 2017.

The flood hazard information is derived directly from the authoritative NFHL web services provided by FEMA. This map was exported on 11/9/2018 at 12:19:55 PM and does not reflect changes or amendments subsequent to this date and time. The NFHL and effective information may change or become superseded by new data over time. This map image is void if the one or more of the following map elements do not appear: basemap imagery, flood zone labels, legend, scale bar, map creation date, community identifiers, FIRM panel number, and FIRM effective date. Map images for unmapped and unmodernized areas cannot be used for regulatory purposes.

Project Information: Located adjacent to 11911 For t W ashington Road, For t W ashington MD

APPENDIX B SOILS REPORT

United States Department of Agriculture

Natural Resources Conservation Service

A product of the National Cooperative Soil Survey, a joint effort of the United States Department of Agriculture and other Federal agencies, State agencies including the Agricultural Experiment Stations, and local participants

Custom Soil Resource Report for

Prince George's County, Maryland

November 9, 2018

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.nrcs.usda.gov/wps/ portal/nrcs/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=nrcs) or your NRCS State Soil Scientist (http://www.nrcs.usda.gov/wps/portal/nrcs/detail/soils/contactus/? cid=nrcs142p2_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

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.

Contents Preface.................................................................................................................... 2 How Soil Surveys Are Made..................................................................................5 Soil Map.................................................................................................................. 8 Soil Map................................................................................................................9 Legend................................................................................................................10 Map Unit Legend................................................................................................ 11 Map Unit Descriptions.........................................................................................11 Prince George's County, Maryland................................................................. 13 LxD—Liverpool-Piccowaxen complex, 5 to 15 percent slopes....................13 PoA—Piccowaxen-Liverpool complex, 0 to 2 percent slopes..................... 15 PrB—Piccowaxen-Urban land complex, 0 to 5 percent slopes................... 16 Soil Information for All Uses...............................................................................18 Soil Properties and Qualities.............................................................................. 18 Soil Erosion Factors........................................................................................18 K Factor, Whole Soil....................................................................................18 Soil Reports........................................................................................................ 22 Soil Chemical Properties.................................................................................22 Chemical Soil Properties............................................................................. 22 Soil Erosion.....................................................................................................26 Conservation Planning................................................................................ 26 References............................................................................................................28

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

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

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.

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.

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MAP LEGEND Area of Interest (AOI) Area of Interest (AOI) Soils Soil Map Unit Polygons Soil Map Unit Lines Soil Map Unit Points Special Point Features Blowout Borrow Pit Clay Spot Closed Depression Gravel Pit Gravelly Spot Landfill Lava Flow Marsh or swamp

MAP INFORMATION The soil surveys that comprise your AOI were mapped at 1:12,000.

Spoil Area Stony Spot Very Stony Spot

Warning: Soil Map may not be valid at this scale.

Wet Spot

Enlargement of maps beyond the scale of mapping can cause misunderstanding of the detail of mapping and accuracy of soil line placement. The maps do not show the small areas of contrasting soils that could have been shown at a more detailed scale.

Other Special Line Features Water Features Streams and Canals Transportation

Please rely on the bar scale on each map sheet for map measurements.

Rails Interstate Highways

Source of Map: Natural Resources Conservation Service Web Soil Survey URL: Coordinate System: Web Mercator (EPSG:3857)

US Routes Major Roads

Maps from the Web Soil Survey are based on the Web Mercator projection, which preserves direction and shape but distorts distance and area. A projection that preserves area, such as the Albers equal-area conic projection, should be used if more accurate calculations of distance or area are required.

Local Roads Background Aerial Photography

Mine or Quarry Miscellaneous Water

This product is generated from the USDA-NRCS certified data as of the version date(s) listed below.

Perennial Water Rock Outcrop

Soil Survey Area: Prince George's County, Maryland Survey Area Data: Version 16, Sep 11, 2018

Saline Spot Sandy Spot

Soil map units are labeled (as space allows) for map scales 1:50,000 or larger.

Severely Eroded Spot Sinkhole

Date(s) aerial images were photographed: 22, 2017

Slide or Slip Sodic Spot

May 3, 2015â&#x20AC;&#x201D;Feb

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.

Custom Soil Resource Report

Map Unit Legend Map Unit Symbol

Map Unit Name

Acres in AOI

Percent of AOI

LxD

Liverpool-Piccowaxen complex, 5 to 15 percent slopes

0.0

0.9%

PoA

Piccowaxen-Liverpool complex, 0 to 2 percent slopes

1.9

39.7%

PrB

Piccowaxen-Urban land complex, 0 to 5 percent slopes

2.8

59.4%

4.7

100.0%

Totals for Area of Interest

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. 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

Custom Soil Resource Report 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.

Custom Soil Resource Report

Prince George's County, Maryland LxDâ&#x20AC;&#x201D;Liverpool-Piccowaxen complex, 5 to 15 percent slopes Map Unit Setting National map unit symbol: 2p28v Elevation: 10 to 370 feet Mean annual precipitation: 40 to 50 inches Mean annual air temperature: 52 to 57 degrees F Frost-free period: 180 to 210 days Farmland classification: Not prime farmland Map Unit Composition Liverpool and similar soils: 45 percent Piccowaxen and similar soils: 40 percent Minor components: 15 percent Estimates are based on observations, descriptions, and transects of the mapunit. Description of Liverpool Setting Landform: Fluviomarine terraces Landform position (three-dimensional): Riser Down-slope shape: Linear Across-slope shape: Linear Parent material: Silty and loamy fluviomarine deposits Typical profile A - 0 to 2 inches: silt loam E - 2 to 5 inches: silt loam Bt1 - 5 to 13 inches: silt loam Bt2 - 13 to 35 inches: clay loam Btg - 35 to 64 inches: sandy clay loam BC - 64 to 74 inches: sandy clay loam Properties and qualities Slope: 5 to 15 percent Depth to restrictive feature: More than 80 inches Natural drainage class: Moderately well drained Runoff class: High Capacity of the most limiting layer to transmit water (Ksat): Moderately low to moderately high (0.06 to 0.60 in/hr) Depth to water table: About 20 to 40 inches Frequency of flooding: None Frequency of ponding: None Available water storage in profile: Low (about 5.7 inches) Interpretive groups Land capability classification (irrigated): None specified Land capability classification (nonirrigated): 4e Hydrologic Soil Group: D Hydric soil rating: No

Custom Soil Resource Report

Description of Piccowaxen Setting Landform: Fluviomarine terraces Landform position (three-dimensional): Riser Down-slope shape: Linear, concave Across-slope shape: Linear Parent material: Silty and loamy fluviomarine deposits Typical profile A - 0 to 4 inches: loam Bt - 4 to 16 inches: silt loam Btg1 - 16 to 28 inches: silt loam Btg2 - 28 to 56 inches: clay loam 2BCg - 56 to 72 inches: fine sandy loam Properties and qualities Slope: 5 to 15 percent Depth to restrictive feature: More than 80 inches Natural drainage class: Somewhat poorly drained Runoff class: Very high 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 10 to 20 inches Frequency of flooding: None Frequency of ponding: Rare Available water storage in profile: High (about 10.1 inches) Interpretive groups Land capability classification (irrigated): None specified Land capability classification (nonirrigated): 4e Hydrologic Soil Group: C/D Hydric soil rating: No Minor Components Croom Percent of map unit: 10 percent Landform: Hillslopes, knolls Landform position (three-dimensional): Side slope Down-slope shape: Linear Across-slope shape: Linear Hydric soil rating: No Marr Percent of map unit: 5 percent Landform: Fluviomarine terraces Landform position (three-dimensional): Riser Down-slope shape: Linear Across-slope shape: Linear Hydric soil rating: No

Custom Soil Resource Report

PoAâ&#x20AC;&#x201D;Piccowaxen-Liverpool complex, 0 to 2 percent slopes Map Unit Setting National map unit symbol: 2p28s Elevation: 10 to 100 feet Mean annual precipitation: 40 to 50 inches Mean annual air temperature: 52 to 57 degrees F Frost-free period: 180 to 210 days Farmland classification: Farmland of statewide importance Map Unit Composition Piccowaxen and similar soils: 55 percent Liverpool and similar soils: 45 percent Estimates are based on observations, descriptions, and transects of the mapunit. Description of Piccowaxen Setting Landform: Fluviomarine terraces, terraces Landform position (three-dimensional): Tread Down-slope shape: Linear Across-slope shape: Linear Parent material: Silty and loamy fluviomarine deposits Typical profile A - 0 to 4 inches: loam Bt - 4 to 16 inches: silt loam Btg1 - 16 to 28 inches: silt loam Btg2 - 28 to 56 inches: clay loam 2BCg - 56 to 72 inches: fine sandy loam Properties and qualities Slope: 0 to 2 percent Depth to restrictive feature: More than 80 inches Natural drainage class: Somewhat poorly drained Runoff class: Very high 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 10 to 20 inches Frequency of flooding: None Frequency of ponding: Rare Available water storage in profile: High (about 10.1 inches) Interpretive groups Land capability classification (irrigated): None specified Land capability classification (nonirrigated): 3w Hydrologic Soil Group: C/D Hydric soil rating: No

Custom Soil Resource Report

Description of Liverpool Setting Landform: Terraces, fluviomarine terraces Landform position (three-dimensional): Tread Down-slope shape: Linear Across-slope shape: Linear Parent material: Silty and loamy fluviomarine deposits Typical profile A - 0 to 2 inches: silt loam E - 2 to 5 inches: silt loam Bt1 - 5 to 13 inches: silt loam Bt2 - 13 to 35 inches: clay loam Btg - 35 to 64 inches: sandy clay loam BC - 64 to 74 inches: sandy clay loam Properties and qualities Slope: 0 to 2 percent Depth to restrictive feature: More than 80 inches Natural drainage class: Moderately well drained Runoff class: Medium Capacity of the most limiting layer to transmit water (Ksat): Moderately low to moderately high (0.06 to 0.60 in/hr) Depth to water table: About 20 to 40 inches Frequency of flooding: None Frequency of ponding: None Available water storage in profile: Low (about 5.7 inches) Interpretive groups Land capability classification (irrigated): None specified Land capability classification (nonirrigated): 2w Hydrologic Soil Group: D Hydric soil rating: No

PrBâ&#x20AC;&#x201D;Piccowaxen-Urban land complex, 0 to 5 percent slopes Map Unit Setting National map unit symbol: 2p28w Elevation: 10 to 100 feet Mean annual precipitation: 40 to 50 inches Mean annual air temperature: 52 to 57 degrees F Frost-free period: 180 to 210 days Farmland classification: Not prime farmland Map Unit Composition Piccowaxen and similar soils: 50 percent Urban land: 30 percent Minor components: 20 percent Estimates are based on observations, descriptions, and transects of the mapunit.

Custom Soil Resource Report

Description of Piccowaxen Setting Landform: Terraces Landform position (three-dimensional): Tread Down-slope shape: Linear, concave Across-slope shape: Linear Parent material: Silty and loamy fluviomarine deposits Typical profile A - 0 to 4 inches: loam Bt - 4 to 16 inches: silt loam Btg1 - 16 to 28 inches: silt loam Btg2 - 28 to 56 inches: clay loam 2BCg - 56 to 72 inches: fine sandy loam Properties and qualities Slope: 0 to 5 percent Depth to restrictive feature: More than 80 inches Natural drainage class: Somewhat poorly drained Runoff class: Very high 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 10 to 20 inches Frequency of flooding: None Frequency of ponding: Rare Available water storage in profile: High (about 10.1 inches) Interpretive groups Land capability classification (irrigated): None specified Land capability classification (nonirrigated): 3w Hydrologic Soil Group: C/D Hydric soil rating: No Description of Urban Land Interpretive groups Land capability classification (irrigated): None specified Land capability classification (nonirrigated): 8 Hydrologic Soil Group: D Hydric soil rating: No Minor Components Liverpool Percent of map unit: 20 percent Landform position (three-dimensional): Tread Hydric soil rating: No

Soil Information for All Uses Soil Properties and Qualities The Soil Properties and Qualities section includes various soil properties and qualities displayed as thematic maps with a summary table for the soil map units in the selected area of interest. A single value or rating for each map unit is generated by aggregating the interpretive ratings of individual map unit components. This aggregation process is defined for each property or quality.

Soil Erosion Factors Soil Erosion Factors are soil properties and interpretations used in evaluating the soil for potential erosion. Example soil erosion factors can include K factor for the whole soil or on a rock free basis, T factor, wind erodibility group and wind erodibility index.

K Factor, Whole Soil Erosion factor K indicates the susceptibility of a soil to sheet and rill erosion by water. Factor K is one of six factors used in the Universal Soil Loss Equation (USLE) and the Revised Universal Soil Loss Equation (RUSLE) to predict the average annual rate of soil loss by sheet and rill erosion in tons per acre per year. The estimates are based primarily on percentage of silt, sand, and organic matter and on soil structure and saturated hydraulic conductivity (Ksat). Values of K range from 0.02 to 0.69. Other factors being equal, the higher the value, the more susceptible the soil is to sheet and rill erosion by water. "Erosion factor Kw (whole soil)" indicates the erodibility of the whole soil. The estimates are modified by the presence of rock fragments.

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MAP LEGEND Area of Interest (AOI) Area of Interest (AOI) Soils Soil Rating Polygons

.24 .28 .32

.02

.37

.05

.43

.10

.49

.15

.55

.17

.64

.20

Not rated or not available

.24 .28 .32 .37 .43 .49 .55 .64 Not rated or not available Soil Rating Lines

MAP INFORMATION Streams and Canals Transportation Rails Interstate Highways US Routes Major Roads Local Roads

The soil surveys that comprise your AOI were mapped at 1:12,000. Warning: Soil Map may not be valid at this scale. Enlargement of maps beyond the scale of mapping can cause misunderstanding of the detail of mapping and accuracy of soil line placement. The maps do not show the small areas of contrasting soils that could have been shown at a more detailed scale.

Background Aerial Photography

Please rely on the bar scale on each map sheet for map measurements.

Soil Rating Points .02

Source of Map: Natural Resources Conservation Service Web Soil Survey URL: Coordinate System: Web Mercator (EPSG:3857)

.05 .10

.15 .17 .20 .24

This product is generated from the USDA-NRCS certified data as of the version date(s) listed below.

.28 .32

.02

.37

.05

.43

.10

.49

.15

.55

.17

.64

.20

Not rated or not available

Soil Survey Area: Prince George's County, Maryland Survey Area Data: Version 16, Sep 11, 2018 Soil map units are labeled (as space allows) for map scales 1:50,000 or larger. Date(s) aerial images were photographed: 22, 2017

May 3, 2015â&#x20AC;&#x201D;Feb

Water Features

Custom Soil Resource Report

Table—K Factor, Whole Soil Map unit symbol

Map unit name

Rating

Acres in AOI

Percent of AOI

LxD

Liverpool-Piccowaxen complex, 5 to 15 percent slopes

.43

0.0

0.9%

PoA

Piccowaxen-Liverpool complex, 0 to 2 percent slopes

.37

1.9

39.7%

PrB

Piccowaxen-Urban land complex, 0 to 5 percent slopes

.37

2.8

59.4%

4.7

100.0%

Totals for Area of Interest

Rating Options—K Factor, Whole Soil Aggregation Method: Dominant Condition Component Percent Cutoff: None Specified Tie-break Rule: Higher Layer Options (Horizon Aggregation Method): Surface Layer (Not applicable)

Custom Soil Resource Report

Soil Reports The Soil Reports section includes various formatted tabular and narrative reports (tables) containing data for each selected soil map unit and each component of each unit. No aggregation of data has occurred as is done in reports in the Soil Properties and Qualities and Suitabilities and Limitations sections. The reports contain soil interpretive information as well as basic soil properties and qualities. A description of each report (table) is included.

Soil Chemical Properties This folder contains a collection of tabular reports that present soil chemical properties. The reports (tables) include all selected map units and components for each map unit. Soil chemical properties are measured or inferred from direct observations in the field or laboratory. Examples of soil chemical properties include pH, cation exchange capacity, calcium carbonate, gypsum, and electrical conductivity.

Chemical Soil Properties This table shows estimates of some chemical characteristics and features that affect soil behavior. These estimates are given for the layers of each soil in the survey area. The estimates are based on field observations and on test data for these and similar soils. Depth to the upper and lower boundaries of each layer is indicated. Cation-exchange capacity is the total amount of extractable cations that can be held by the soil, expressed in terms of milliequivalents per 100 grams of soil at neutrality (pH 7.0) or at some other stated pH value. Soils having a low cation-exchange capacity hold fewer cations and may require more frequent applications of fertilizer than soils having a high cation-exchange capacity. The ability to retain cations reduces the hazard of ground-water pollution. Effective cation-exchange capacity refers to the sum of extractable cations plus aluminum expressed in terms of milliequivalents per 100 grams of soil. It is determined for soils that have pH of less than 5.5. Soil reaction is a measure of acidity or alkalinity. It is important in selecting crops and other plants, in evaluating soil amendments for fertility and stabilization, and in determining the risk of corrosion. Calcium carbonate equivalent is the percent of carbonates, by weight, in the fraction of the soil less than 2 millimeters in size. The availability of plant nutrients is influenced by the amount of carbonates in the soil. Gypsum is expressed as a percent, by weight, of hydrated calcium sulfates in the fraction of the soil less than 20 millimeters in size. Gypsum is partially soluble in water. Soils that have a high content of gypsum may collapse if the gypsum is removed by percolating water.

Custom Soil Resource Report Salinity is a measure of soluble salts in the soil at saturation. It is expressed as the electrical conductivity of the saturation extract, in millimhos per centimeter at 25 degrees C. Estimates are based on field and laboratory measurements at representative sites of nonirrigated soils. The salinity of irrigated soils is affected by the quality of the irrigation water and by the frequency of water application. Hence, the salinity of soils in individual fields can differ greatly from the value given in the table. Salinity affects the suitability of a soil for crop production, the stability of soil if used as construction material, and the potential of the soil to corrode metal and concrete. Sodium adsorption ratio (SAR) is a measure of the amount of sodium (Na) relative to calcium (Ca) and magnesium (Mg) in the water extract from saturated soil paste. It is the ratio of the Na concentration divided by the square root of one-half of the Ca + Mg concentration. Soils that have SAR values of 13 or more may be characterized by an increased dispersion of organic matter and clay particles, reduced saturated hydraulic conductivity and aeration, and a general degradation of soil structure.

Custom Soil Resource Report

Chemical Soil Properties–Prince George's County, Maryland Map symbol and soil name

Depth

Cationexchange capacity

Effective cationexchange capacity

Soil reaction

Calcium carbonate

Gypsum

Salinity

meq/100g

Pct

mmhos/cm

Sodium adsorption ratio

LxD—Liverpool-Piccowaxen complex, 5 to 15 percent slopes Liverpool

Piccowaxen

0-2

4.0-20

3.0-10

3.7-6.5

2-5

2.0-7.0

1.0-7.0

3.9-6.0

5-13

5.0-11

2.0-11

3.9-5.0

13-35

7.0-17

5.0-17

3.8-4.8

35-64

1.0-17

0.1-13

3.8-4.8

64-74

1.0-14

0.1-13

3.8-4.8

0-4

6.0-22

3.0-10

4.4-6.0

4-16

2.0-5.0

1.0-3.0

3.6-5.2

16-28

5.0-9.0

3.0-5.0

3.6-5.0

28-56

12-16

9.0-12

3.6-5.0

56-72

2.0-14

2.0-12

3.6-5.3

Custom Soil Resource Report

Chemical Soil Properties–Prince George's County, Maryland Map symbol and soil name

Depth

Cationexchange capacity

Effective cationexchange capacity

Soil reaction

Calcium carbonate

Gypsum

Salinity

meq/100g

Pct

mmhos/cm

Sodium adsorption ratio

PoA—Piccowaxen-Liverpool complex, 0 to 2 percent slopes Piccowaxen

Liverpool

0-4

6.0-22

3.0-10

4.4-6.0

4-16

2.0-5.0

1.0-3.0

3.6-5.2

16-28

5.0-9.0

3.0-5.0

3.6-5.0

28-56

12-16

9.0-12

3.6-5.0

56-72

2.0-14

2.0-12

3.6-5.3

0-2

4.0-20

3.0-10

3.7-6.5

2-5

2.0-7.0

1.0-7.0

3.9-6.0

5-13

5.0-11

2.0-11

3.9-5.0

13-35

7.0-17

5.0-17

3.8-4.8

35-64

1.0-17

0.1-13

3.8-4.8

64-74

1.0-14

0.1-13

3.8-4.8

0-4

6.0-22

3.0-10

4.4-6.0

4-16

2.0-5.0

1.0-3.0

3.6-5.2

16-28

5.0-9.0

3.0-5.0

3.6-5.0

28-56

12-16

9.0-12

3.6-5.0

56-72

2.0-14

2.0-12

3.6-5.3

—

PrB—Piccowaxen-Urban land complex, 0 to 5 percent slopes Piccowaxen

Urban land

Custom Soil Resource Report

Soil Erosion This folder contains a collection of tabular reports that present soil erosion factors and groupings. The reports (tables) include all selected map units and components for each map unit. Soil erosion factors are soil properties and interpretations used in evaluating the soil for potential erosion. Example soil erosion factors can include K factor for the whole soil or on a rock free basis, T factor, wind erodibility group and wind erodibility index.

Conservation Planning This report provides those soil attributes for the conservation plan for the map units in the selected area. The report includes the map unit symbol, the component name, and the percent of the component in the map unit. It provides the soil description along with the slope, runoff, T Factor, WEI, WEG, Erosion class, Drainage class, Land Capability Classification, and the engineering Hydrologic Group and the erosion factors Kf, the representative percentage of fragments, sand, silt, and clay in the mineral surface horizon. Missing surface data may indicate the presence of an organic surface layer. Further information on these factors can be found in the National Soil Survey Handbook section 618 found at the url http:// www.nrcs.usda.gov/wps/portal/nrcs/detail/soils/ref/?cid=nrcs142p2_054223#00 .

Custom Soil Resource Report Soil properties and interpretations for conservation planning. The surface mineral horizon properties are displayed. Organic surface horizons are not displayed. Conservation Planning–Prince George's County, Maryland Map symbol and soil name

Pct. of Slope map RV unit

USLE Slope Length ft.

Runoff

T Fact or

WEI

WEG

Erosion

Drainage

NIRR LCC

Hydro logic Group Depths in.

Surface

High

Class 2

Moderately well drained

0-1

.43

Kf Fact or

Fragments RV

Sand RV

Silt RV

Clay RV

LxD—LiverpoolPiccowaxen complex, 5 to 15 percent slopes Liverpool

10.0 —

Piccowaxen

8.0 —

Very high

Class 2

Somewhat poorly drained

C/D

0-3

.37

Piccowaxen

1.0 —

Very high

Class 1

Somewhat poorly drained

C/D

0-3

.37

Liverpool

1.0 —

Medium

Class 1

Moderately well drained

0-1

.43

1.0 —

Very high

Class 1

Somewhat poorly drained

C/D

0-3

.37

PoA—PiccowaxenLiverpool complex, 0 to 2 percent slopes

PrB—Piccowaxen-Urban land complex, 0 to 5 percent slopes Piccowaxen

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.nrcs.usda.gov/wps/portal/ nrcs/detail/national/soils/?cid=nrcs142p2_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.nrcs.usda.gov/wps/portal/nrcs/detail/national/soils/?cid=nrcs142p2_053577 Soil Survey Staff. 2010. Keys to soil taxonomy. 11th edition. U.S. Department of Agriculture, Natural Resources Conservation Service. http:// www.nrcs.usda.gov/wps/portal/nrcs/detail/national/soils/?cid=nrcs142p2_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.nrcs.usda.gov/wps/portal/nrcs/detail/soils/ home/?cid=nrcs142p2_053374 United States Department of Agriculture, Natural Resources Conservation Service. National range and pasture handbook. http://www.nrcs.usda.gov/wps/portal/nrcs/ detail/national/landuse/rangepasture/?cid=stelprdb1043084

Custom Soil Resource Report United States Department of Agriculture, Natural Resources Conservation Service. National soil survey handbook, title 430-VI. http://www.nrcs.usda.gov/wps/portal/ nrcs/detail/soils/scientists/?cid=nrcs142p2_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.nrcs.usda.gov/wps/portal/nrcs/detail/national/soils/? cid=nrcs142p2_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/Internet/FSE_DOCUMENTS/nrcs142p2_052290.pdf

APPENDIX C FOREST STAND DATA AND STRUCTURE ANALYSIS SHEETS

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Pignut Hickory

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Sweetgum, Red Oak, Willow Oak, Carex sp.

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258

258 0

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258 14

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4Ã¿ 8 Ã¿2 Ã¿ 144 Ã¿ 5% Ã¿ 8!3 4Ã¿3 25

8 8 Ã¿ 148Ã¿ Ã¿ 8 147Ã¿Ã¿ 130

144Ã¿ 34 4 Ã¿2 Ã¿ 144 2 Ã¿ 144 Ã¿2 Ã¿ 144 Ã¿2 Ã¿ 144 Ã¿2 Ã¿ 144 12304$Ã¿9 % #2404$Ã¿9 % ./2.804$9 % .J21404$Ã¿9 % (Ã¿5/$Ã¿9 % 12 Ã¿02 5 2 White Oak

Red Maple

2 3

Swamp White Oak American Elm Pignut Hickory

Red Oak

258 Ã¿ ! 41Ã¿2 Ã¿ 144 Ã¿341Ã¿ 4Ã¿ 8 ! 41Ã¿2 Ã¿ 58 9 "Ã¿9489Ã¿ 5144 Ã¿#$Ã¿9 %Ã¿21Ã¿ "148541 . .//Ã¿ 0Ã¿ 8!3 4 7

258

* 5Ã¿2 Ã¿ 2!!2 Ã¿7 941 5216Ã¿ 34 4 Ã¿5621/6

Greenbriar, Pignut Hickory Red Oak, Wild Azalea

* 5Ã¿2 Ã¿ 41 8 42 Ã¿ 34 4 Ã¿/6256

White Oak, American Holly Sweetgum

* 5Ã¿2 Ã¿+ ,8 ,4Ã¿ 34 4

-Ã¿ 8 236Ã¿ 2,418"4

& ' 80 80

258

-Ã¿+ ,8 ,4Ã¿ 2,41

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60 90 90 80 0

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258

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20 10 10 10 10 12 20 30 30 30 30

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258

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White Oak

Pignut Hickory Southern Red Oak Red Maple

258

4 1

Willow Oak

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* 5Ã¿2 Ã¿+ ,8 ,4Ã¿ 34 4

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Beech, Pignut Hickory, Red Maple

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258

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70 70 80 80 90 78 0

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258

25 30 30 10 30 25

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258 10

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Red Oak

1 1

Red Maple

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Paw Paw, Wild Azalea, Highbush Blueberry

Beech

1 1

White Oak

258

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258

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APPENDIX D AGENCY CORRESPONDENCE

CV, Inc.

1395 Piccard Drive Suite 370 Rockville, Maryland 20850 Ph: (301) 637.2510 Fax: (240) 252.5612

www.CVtnc.com

November 9, 2018

Ms. Lori Byrne MD DNR-Wildlife Services Tawes State Office Building, E-1 580 Taylor Avenue Annapolis, Maryland 21404 Re:

Harbor View Property Prince George's County, Maryland

Dear Ms. Byrne: CV Inc is preforming a Forest Stand Delineation for the above reference property in Fort Washington, Prince George's County, Maryland. A Vicinity map of the site is enclosed for your reference. We would appreciate receiving any information you can provide through your environmental review process. If you have any questions or require any additional information, please do not hesitate to call (301) 637-2510. Thank you for your time and effort.

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Richard Hammond Landscape Architect/Planner CV, Inc.

Harbor View Vicinity Map Prince George's County, Maryland November 2018

Data Sources:

Project Information: Located adjacent to 11911 Fort Washington Road, Fort Washington MD

United States Department of the Interior FISH AND WILDLIFE SERVICE Chesapeake Bay Ecological Services Field Office 177 Admiral Cochrane Drive Annapolis, MD 21401-7307 Phone: (410) 573-4599 Fax: (410) 266-9127 http://www.fws.gov/chesapeakebay/ http://www.fws.gov/chesapeakebay/endsppweb/ProjectReview/Index.html

In Reply Refer To: Consultation Code: 05E2CB00-2019-SLI-0360 Event Code: 05E2CB00-2019-E-00803 Project Name: Harbor View

November 20, 2018

Subject: List of threatened and endangered species that may occur in your proposed project location, and/or may be affected by your proposed project To Whom It May Concern: The enclosed species list identifies threatened, endangered, proposed and candidate species, as well as proposed and final designated critical habitat, that may occur within the boundary of your proposed project and/or may be affected by your proposed project. This species list fulfills the requirements of the U.S. Fish and Wildlife Service (Service) under section 7(c) of the Endangered Species Act (Act) of 1973, as amended (16 U.S.C. 1531 et seq.). New information based on updated surveys, changes in the abundance and distribution of species, changed habitat conditions, or other factors could change this list. Please feel free to contact us if you need more current information or assistance regarding the potential impacts to federally proposed, listed, and candidate species and federally designated and proposed critical habitat. Please note that under 50 CFR 402.12(e) of the regulations implementing section 7 of the Act, the accuracy of this species list should be verified after 90 days. This verification can be completed formally or informally as desired. The Service recommends that verification be completed by visiting the ECOS-IPaC website at regular intervals during project planning and implementation for updates to species lists and information. An updated list may be requested through the ECOS-IPaC system by completing the same process used to receive the enclosed list. The purpose of the Act is to provide a means whereby threatened and endangered species and the ecosystems upon which they depend may be conserved. Under sections 7(a)(1) and 7(a)(2) of the Act and its implementing regulations (50 CFR 402 et seq.), Federal agencies are required to utilize their authorities to carry out programs for the conservation of threatened and endangered species and to determine whether projects may affect threatened and endangered species and/or designated critical habitat.

11/20/2018

Event Code: 05E2CB00-2019-E-00803

A Biological Assessment is required for construction projects (or other undertakings having similar physical impacts) that are major Federal actions significantly affecting the quality of the human environment as defined in the National Environmental Policy Act (42 U.S.C. 4332(2) (c)). For projects other than major construction activities, the Service suggests that a biological evaluation similar to a Biological Assessment be prepared to determine whether the project may affect listed or proposed species and/or designated or proposed critical habitat. Recommended contents of a Biological Assessment are described at 50 CFR 402.12. If a Federal agency determines, based on the Biological Assessment or biological evaluation, that listed species and/or designated critical habitat may be affected by the proposed project, the agency is required to consult with the Service pursuant to 50 CFR 402. In addition, the Service recommends that candidate species, proposed species and proposed critical habitat be addressed within the consultation. More information on the regulations and procedures for section 7 consultation, including the role of permit or license applicants, can be found in the "Endangered Species Consultation Handbook" at: http://www.fws.gov/endangered/esa-library/pdf/TOC-GLOS.PDF Please be aware that bald and golden eagles are protected under the Bald and Golden Eagle Protection Act (16 U.S.C. 668 et seq.), and projects affecting these species may require development of an eagle conservation plan (http://www.fws.gov/windenergy/ eagle_guidance.html). Additionally, wind energy projects should follow the wind energy guidelines (http://www.fws.gov/windenergy/) for minimizing impacts to migratory birds and bats. Guidance for minimizing impacts to migratory birds for projects including communications towers (e.g., cellular, digital television, radio, and emergency broadcast) can be found at: http:// www.fws.gov/migratorybirds/CurrentBirdIssues/Hazards/towers/towers.htm; http:// www.towerkill.com; and http://www.fws.gov/migratorybirds/CurrentBirdIssues/Hazards/towers/ comtow.html. We appreciate your concern for threatened and endangered species. The Service encourages Federal agencies to include conservation of threatened and endangered species into their project planning to further the purposes of the Act. Please include the Consultation Tracking Number in the header of this letter with any request for consultation or correspondence about your project that you submit to our office. Attachment(s): ƒ Official Species List ƒ USFWS National Wildlife Refuges and Fish Hatcheries ƒ Wetlands

11/20/2018

Event Code: 05E2CB00-2019-E-00803

Official Species List This list is provided pursuant to Section 7 of the Endangered Species Act, and fulfills the requirement for Federal agencies to "request of the Secretary of the Interior information whether any species which is listed or proposed to be listed may be present in the area of a proposed action". This species list is provided by: Chesapeake Bay Ecological Services Field Office 177 Admiral Cochrane Drive Annapolis, MD 21401-7307 (410) 573-4599

11/20/2018

Event Code: 05E2CB00-2019-E-00803

Project Summary Consultation Code: 05E2CB00-2019-SLI-0360 Event Code:

05E2CB00-2019-E-00803

Project Name:

Harbor View

Project Type:

DEVELOPMENT

Project Description: The Harbor View property is a 4.69 acre undeveloped lot. The lot is fully wooded. The Developer intends to subdivide and construct single family residential houses. Project Location: Approximate location of the project can be viewed in Google Maps: https:// www.google.com/maps/place/38.73044990800357N77.00622547711586W

Counties: Prince George's, MD

11/20/2018

Event Code: 05E2CB00-2019-E-00803

Endangered Species Act Species There is a total of 0 threatened, endangered, or candidate species on this species list. Species on this list should be considered in an effects analysis for your project and could include species that exist in another geographic area. For example, certain fish may appear on the species list because a project could affect downstream species. IPaC does not display listed species or critical habitats under the sole jurisdiction of NOAA Fisheries1, as USFWS does not have the authority to speak on behalf of NOAA and the Department of Commerce. See the "Critical habitats" section below for those critical habitats that lie wholly or partially within your project area under this office's jurisdiction. Please contact the designated FWS office if you have questions. 1. NOAA Fisheries, also known as the National Marine Fisheries Service (NMFS), is an office of the National Oceanic and Atmospheric Administration within the Department of Commerce.

Critical habitats THERE ARE NO CRITICAL HABITATS WITHIN YOUR PROJECT AREA UNDER THIS OFFICE'S JURISDICTION.

11/20/2018

Event Code: 05E2CB00-2019-E-00803

USFWS National Wildlife Refuge Lands And Fish Hatcheries Any activity proposed on lands managed by the National Wildlife Refuge system must undergo a 'Compatibility Determination' conducted by the Refuge. Please contact the individual Refuges to discuss any questions or concerns. THERE ARE NO REFUGE LANDS OR FISH HATCHERIES WITHIN YOUR PROJECT AREA.

11/20/2018

Event Code: 05E2CB00-2019-E-00803

Wetlands Impacts to NWI wetlands and other aquatic habitats may be subject to regulation under Section 404 of the Clean Water Act, or other State/Federal statutes. For more information please contact the Regulatory Program of the local U.S. Army Corps of Engineers District. Please note that the NWI data being shown may be out of date. We are currently working to update our NWI data set. We recommend you verify these results with a site visit to determine the actual extent of wetlands on site. THERE ARE NO WETLANDS WITHIN YOUR PROJECT AREA.

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Data Sources:

Project Information: Located adjacent to 11911 Fort Washington Road, Fort Washington MD

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1395 Piccard Drive Suite 370 Rockville, Maryland 20850 Ph: (301) 637.2510 Fax: (240) 252.5612

www.CVInc.com

November 19, 2018 Ms. Beth Cole Maryland Historical Trust 100 Community Place, 3rd Floor Crownsville, MD 21032 Re:

Harbor View, Fort Washington Prince Georgeâ&#x20AC;&#x2122;s County, Maryland

Dear Ms. Cole, CV Inc is preparing an FSD for the above referenced property in Fort Washington, Prince Georgeâ&#x20AC;&#x2122;s County, Maryland. As part of this process, we are requesting any information you may have on the presence of historic or cultural resources onsite. A complete package including Aerial Photography, USGS Quad Map, a Vicinity Map, Photographs of the site, and tax account information is included. The site is an undeveloped, wooded lot spanning 4.69 acres. The developer intends to subdivide the lot and develop single family residences. There are currently no permits active on site. An NRI and a Preliminary plan are in the process of being submitted. If you have any questions or require any additional information, please do not hesitate to call (301) 637-2510. Thank you for your time and effort. Sincerely,

Richard Hammond Landscape Architect/Planner CV, Inc.

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Data Sources:

Project Information: Located adjacent to 11911 Fort Washington Road, Fort Washington MD

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Plot #1 – Facing West

Plot #2 – Downed Woody Debris

Plot #3

Plot #4

APPENDIX E QUALIFICATIONS

APPENDIX F PHOTOGRAPHIC DOCUMENTATION

Plot #1 – Facing West

Plot #2 – Downed Woody Debris

Plot #3

Plot #4

NORTH

VICINITY MAP:

GENERAL NOTES

1. THIS SITE IS ZONED R-R AND IS LOCATED IN THE DEVELOPING TIER AS DEFINED IN THE APPROVED GENERAL PLAN. 2. THE SOURCE OF THE PROPERTY BOUNDARIES ON THIS PLAN IS FROM A SURVEY DATED DEC. 18, 2017 AND PREFROMED BY CURRIE AND ASSOCIATES. 3. THE TOPOGRAPHY SHOWN ON THIS PLAN IS FROM A SURVERY DATED DEC. 18, 2017 AND PREFORMED BY CURRIE AND ASSOCIATES. 4. THE SOURCE OF THE SOILS INFORMATION ON THIS PLAN IS FROM THE USDA NRCS WEB SOIL SURVEY (WSS) IN A CUSTOM SOIL RESOURCE REPORT FOR AN AREA OF INTEREST (AOI) ESTABLISHED FOR THE STUDY SITE ONLY AND GENERATED ON NOV. 9, 2018. 5. NO COUNTY REGULATED 100-YEAR FLOODPLAIN IS LOCATED ON SITE PER DPIE LETTER OF VERIFICATION DATED NOV. 26, 2018. 6. NO WETLANDS OR STREAMS ARE LOCATED ON-SITE AS FIELD VERIFIED BY ROBERT BOYD, PLA AICP.

7. THIS SITE IS NOT WITHIN A SENSITIVE SPECIES PROTECTION REVIEW AREA BASED ON A REVIEW OF THE SSPRA GIS LAYER PREPARED BY THE HERITAGE AND WILDLIFE SERVICE, MARYLAND DEPARTMENT OF NATURAL RESOURCES A LETTER WAS SENT ON NOVEMBER 9TH TO MD DNR, HOWEVER A RESPONSE HAS NOT BEEN RECEIVED AS OF THIS SUBMISSION.

FOREST STAND - A 2.89-acres (125,888 sq.ft.) Medium Priority for Preservation

8. THE SITE DOES NOT INCLUDE FOREST INTERIOR DWELLING SPECIES HABITAT. 9. THE SITE IS NOT SUBJECT TO A PREVIOUSLY APPROVED TCP. 10. THERE ARE NINE (9) SPECIMEN, CHAMPION, AND/OR HISTORIC TREES LOCATED ON THE PROPERTY. THESE TREES WERE LOCATED USING FIELD OBSERVATIONS.

11.MARLBORO CLAY AND CHRISTIANA COMPLEX ARE NOT FOUND TO OCCUR ON OR WITHIN THE VICINITY OF THIS PROPERTY.

12. THE SITE DOES NOT CONTAIN WETLANDS OF SPECIAL STATE CONCERN AS DEFINED IN COMAR 26.23.06.01.

FOREST STAND - B 1.80-acres (78,408 sq.ft.) Medium Priority for Preservation

13. THE SITE DOES NOT CONTAIN A TIER II WATERBODY AS DEFINED IN COMAR 26.08.02.04 14. THE SITE IS NOT LOCATED WITHIN A STRONGHOLD WATERSHED AS ESTABLISHED BY MD DNR.

15. THERE ARE NO SCENIC OR HISTORIC ROADS LOCATED ON OR ADJACENT TO THE PROPERTY. 16. THE SUBJECT PROPERTY IS NOT LOCATED WITHIN A REGISTERED HISTORIC DISTRICT. 17. THERE ARE NO KNOWN ARCHEOLOGICAL SITES LOCATED ON THE SUBJECT PROPERTY; HOWEVER, THE SUBJECT PROPERTY HAS NOT BEEN SURVEYED FOR ARCHELOGICAL RESOURCES AND A PHASE I ARCHEOLOGY REPORT MAY BE REQUIRED DURING SUBSEQUENT DEVELOPMENT REVIEW PROCESS. 18. THE SITE IS NOT LOCATED IN THE VICINITY OF ANY MASTER PLANNED ROADWAY DESIGNATED AS ARTERIAL OR HIGHER. 19. THE SUBJECT PROPERTY IS NOT LOCATED WITHIN THE 2008 AIR INSTALLATION COMPATIBLE USE ZONE (AICUZ) STUDY FOR ANDREWS AIR FORCE BASE. 20. THE SITE IS NOT LOCATED WITHIN AN AVIATION POLICY AREA (APA). 21. THE SITE IS NOT LOCATED WITHIN THE CHESAPEAKE BAY CRITICAL AREA (CBCA). 22. AN APPROVED NRI IS VALID FOR FIVE YEARS FROM THE DATE OF SIGNATURE BY STAFF, OR UNTIL INFORMATION USED TO PREPARE THE NRI CHANGES. NRIS WILL BE REQUIRED TO BE REVISED AND RE-APPROVED IF THE BASE INFORMATION CHANGES SIGNIFICANTLY. APPROVAL OF THIS NRI IN NO WAY IMPARTS ANY OTHER DEVELOPMENT APPLICATION APPROVAL. FOREST STAND SUMMARY TABLE:

LEGEND SITE STATISTICS

Property Boundary

FOREST STAND DESCRIPTION

PoA(C/D)

Existing Soils

GROSS TRACT AREA EXISTING 100-YEAR FLOODPLAIN EXISTING WOODLAND IN FLOODPLAIN EXISTING WOODLAND IN NET TRACT EXISTING WOODLAND TOTAL EXISTING PMA REGULATED STREAMS

FOREST STAND A - 2.89 acres - Mixed Oak - Mid to Late Successional - Priority Retention - Medium FOREST STAND B - 1.80 acres - Mixed Oak - Beech - Mid to Late Succesional - Priority Retention - Medium Total Woodland On-Site - 4.69 acres

PrB(C/D) CRZ CRZ

Total Site Acreage - 4.69 acres

Specimen Tree (ST-#)and Critical Root Zone

1. Dominant species/ Codominant species 2. Successional Stage 3. Basal Area in s.f. per acre 4. Size class of dominant species 5. Percent of canopy closure 6. Number of tree species per acre 7. Common Understory Species 8. % of Understory 3'-20' 9. # of woody plant species 3'-20' 10. Common herbaceous species 0'-3' 11. % of herbaceous species 0'-3' 12. List of major invasive plant species and cover 13. # of standing dead trees > 6"

Red Oak, White Oak

Red Oak, White Oak American Beech Mid-to-Late 130 10-17.9" DBH 74% 6 Red Maple, Paw Paw, Wild Azalea 21.5% 6 Holly, White Oak, Greenbriar

Mid-to-Late 127.5 10-17.9" DBH 80% 6 Pignut Hickory, Holly, Sweetgum 14% 8 Holly, White Oak, Sweetgum Red Oak 21% <5% - Japanese Stiltgrass 1

15%

FOREST ANALYSIS AND PRIORITIES SUMMARY TABLE:

SOILS DATA

Structure (Out of 20)

Condition (Out of 20)

Location (Out of 20) 10

Total (Out of 60) 37

Priority For Preservation Medium

Priority For Restoration

Medium

Symbol

Soil Name

PoA

Piccowaxen - Liverpool Complex, 0 - 2% Slopes

Existing Treeline PrB

SPECIMEN TREES

PLEASE NOTE: Forest Interior Dwelling Species (FIDS) Buffer

Stand A Forest Stand Boundary

The location of offsite features is estimated based off of review of available GIS and other mapping data. CV Inc does not certify the accuracy or existence of offsite environmental and other features or associated buffers.

TREE # ST-1 ST-2 ST-3 ST-4 ST-5 ST-6 ST-7 ST-8 ST-9

COMMON NAME Red Oak White Oak Red Oak White Oak White Oak White Oak Southern Red Oak White Oak Bur Oak

BOTANICAL NAME Quercus rubra Quercus alba Quercus rubra Quercus alba Quercus alba Quercus alba Quercus falcata Quercus alba Quercus macrocarpa

DBH(IN) 34 30 32 33 39 36 30 38 30

Hydrologic Hydric Rating Soils Group

APPROVAL

0.37

Low

LxD

Forest Stand Data Plot

K-Factor Drainage Class

M-NCPPC Prince George's Planning Department Environmental Planning Sections NATURAL RESOURCES INVENTORY

Low

>15% slopes

Stand B

NO WETLANDS OR STREAMS WERE IDENTIFIED ONSITE.

STAND

4.69 acres (203,667 sq.ft.) 0.00 acres (0.00 sq.ft.) 0.00 acres 4.69 acres (203,667 sq.ft.) 4.69 acres (203,667 sq.ft.) 0.00 acres (0.00 sq.ft.) 0.00 l.f.(0.00 sq.ft.)

Forest Stand Number

CONDITION Fair Good Good Good Good Fair Good Good Good

Liverpool - Piccowaxen Complex, 5 - 15% slopes

Piccowaxen - Urban Land Complex, 5-10% slopes

Somewhat Poorly Drained

C/D

Not Hydric

NRI-XXX-XXXX Staff Signature

0.43

Moderately Well Drained

Not Hydric

0.37

Somewhat Poorly Drained

C/D

Not Hydric

Date

Initial Approval 01 Revision 02 Revision

HARBOR VIEW DEVELOPER CORP.

HARBOR VIEW

C V , I N C.

NATURAL RESOURCE INVENTORY PLAN

20181035