Description: "This is a searchable database representing over 40 years of hydrogeologic information based on yield testing required for new and existing public water supply sources in Vermont. The VRWA final report (the basis for the development of SQL database) was limited to currently active or permitted drilled PCWS sources. This represents 203 PCWS sources and 1,082 observation points evaluated across the state up to 2008. The results of the study indicate that, overall, groundwater interference is not a chronic problem in Vermont. However, unacceptable interference – where a specific observation well source could no longer meet its design demand – was noted in several instances in areas of higher concentrations of PCWS sources. This database is dynamic and will be populated by the most current information available as part of the ongoing DEC Source Permitting process. Public water system source testing information will be added soon for evaluations completed from 2008 to present. These data may include other water systems where interference analyses were done such as Non-Transient Non-Community and Transient Non-Community wells. Since late 1980, protocols for the testing of new PCWS groundwater sources (e.g., drilled bedrock wells, drilled gravel wells), have existed in Vermont. These protocols were initially developed by the VDOH, which at that time was the regulatory body for new PCWS sources in Vermont. Since the transfer of PCWS regulatory authority to the WSD in 1991, requirements associated with the testing and permitting of new PCWS sources has been codified in the Environmental Protection Rules, Chapter 21: The Water Supply Rule. One aspect of the Source Permitting process is measuring and evaluating whether pumping a proposed PCWS will withdraw enough water to reduce water levels in the surrounding area. The majority of PCWS sources in Vermont are wells completed in fractured crystalline bedrock aquifers, with a more limited number completed in sand and gravel aquifers present in some valley locations. Due to the non-homogenous, anisotropic nature of these aquifers, the impact of water withdrawal on nearby private and public wells and springs is difficult to predict unless measured in the field. By monitoring water levels in nearby water supply wells and springs during a constant discharge test (pumping test) the observed or estimated impact can be predicted. The impact to existing drinking water supplies is called Interference and can range from non-existent to adverse – where there isn’t enough water to meet the demands of the current use. Adverse or unacceptable interference is required to be mitigated before a Source Permit can be issued. Existing source evaluation reports prepared between 1980 and 2008 by the environmental consulting community were reviewed to develop a geodatabase that includes key information about the pumped wells and observation wells and springs monitored during these tests. This information includes specific pumping test information, derived values such as aquifer transmissivity and storativity, the degree of interference noted at observation locations, and a determination of acceptable versus unacceptable interference. The database currently contains data from 1980-2008. Data from tests conducted from 2009 to the present will be entered over the next several months."
Description: Assist the VT Agency of Natural Resources and Water Well Advisory Committee address well drilling and groundwater issues. The database is the result of the Water Well Driller Licensing Rule. The rule is adopted under the authority of 10 Vermont Statutes Annotated (V.S.A.) §1390-1410. The purpose of the rule is to protect public health and the environment by providing for the licensing of water and monitoring well drillers, the recording and reporting of each well drilled, and the closure of abandoned wells. This GIS layer consists of the geographic location of all well completion reports filed with state since 1966. Licensed Well Drillers are required to submit reports for each well (drinking water, monitor well, geothermal or closure of well) and location. The well reports include wells for single family homes, public buildings, subdivisions and public water supplies (Public Community, Non-Transient Non-Community and Transient Non-Community), along with wells deepened or closed (abandoned). There are over 110,000 reports. The well data and locations are drawn from the well completion report database. The database consisted of paper records and maps but was converted in 1995 to an electronic database for the tabular data and a GIS layer for locations tied to Well Report or Tag number.
Description: This GIS layer consists of the geographic location of active and inactive public (Community, non-transient non-community and transient non-community) water sources labeled by the Water System Identification Number (WSID) and source number (i.e. WL001 or IN002). The water source data and locations are drawn from the State Drinking Water database (SDWIS). The water sources are wells, springs and surface water intakes that predate regulations developed in the 1970s to the present. SDWIS is the repository for state and federal information collected from and about each public water system in Vermont, including bulk and bottled water facilities along with water production and water quality data. "
Color: [0, 132, 168, 255] Background Color: N/A Outline Color: N/A Vertical Alignment: bottom Horizontal Alignment: center Right to Left: false Angle: 0 XOffset: 0 YOffset: 0 Size: 8 Font Family: Georgia Font Style: normal Font Weight: normal Font Decoration: none
Description: This layer contains permits issued by the Stormwater Management Program for impervious surfaces (operational permits) or industrial activities (MSGP). Construction permits (9020, 9001, and INC) are temporary permits and not included as part of this dataset. Permits contained in this dataset have been issued according to the Stormwater Permits Database. Additional information, including a link to the permit document, issued date, and expiration date are available for each permit.
Description: This layer contains pending permits by the Stormwater Management Program for impervious surfaces (operational permits) or industrial activities (MSGP). Construction permits (9020, 9001, and INC) are temporary permits and not included as part of this dataset. Permits contained in this dataset have been issued according to the Stormwater Permits Database. Additional information, including a link to the permit document, issued date, and expiration date are available for each permit. information, including a link to the permit document, issued date, and expiration date are available for each permit.
Description: This dataset is derived from a project by the Vermont Center for Ecostudies(VCE) and Arrowwood Environmental(AE) to map vernal pools throughout the state of Vermont. AE and VCE are mapping locations of potential vernal pools throughout Vermont, and recruiting a corps of volunteers to field-verify the presence of these potential pools. In the process, we will develop a GIS layer of potential and known vernal pools, as well as a database populated with biological and physical attributes of each verified pool. With partial funding from the Vermont State Wildlife Grants Program, potential vernal pools will be identified using color infrared aerial photographs.
Copyright Text: Arrowwood Environmental and Vermont Center for Ecostudies
Description: This dataset is derived from a project by the Vermont Center for Ecostudies(VCE) and Arrowwood Environmental(AE) to map vernal pools throughout the state of Vermont. AE and VCE are mapping locations of potential vernal pools throughout Vermont, and recruiting a corps of volunteers to field-verify the presence of these potential pools. In the process, we will develop a GIS layer of potential and known vernal pools, as well as a database populated with biological and physical attributes of each verified pool. With partial funding from the Vermont State Wildlife Grants Program, potential vernal pools will be identified using color infrared aerial photographs.
Copyright Text: Arrowwood Environmental and Vermont Center for Ecostudies
Description: Identification of currently designated ORWs as well as prospective candidates for possible designation at a later date. ORWs are designated by the Secretary of the Agency of Natural resources under 10 VSA 1424a.
Description: The GIS dataset displays a representative area covered by the Shoreland Protection Act. Lakes, over 10 acres, managed by our Lakes and Ponds Management and Protection Program through its Lake Inventory database are included. Buffered zones (Lakeside and Upland) were created from the National Hydrography Dataset when available. Buffered portions, away from the lake and intersected by the public highway, have been removed as they are exempted from permitting.
Description: Identification of currently designated ORWs as well as prospective candidates for possible designation at a later date. ORWs are designated by the Secretary of the Agency of Natural resources under 10 VSA 1424a.
Description: The stream geomorphic assessment (SGA) is a physical assessment competed by geomorphologists to determine the condition and sensitivity of a stream. The SGA Phase 2 Segment Breaks are points that indicate where the Phase 1 SGA reach was "segmented" into smaller Phase 2 segments. These segments are determined in the field and are based on changes in topography, slope and valley setting that were not found in phase 1, and on changes in condition found in the field. Where there found in the field a significant change in any of the above there is a segment break created.
Color: [0, 255, 0, 255] Background Color: N/A Outline Color: N/A Vertical Alignment: bottom Horizontal Alignment: center Right to Left: false Angle: 0 XOffset: 0 YOffset: 0 Size: 8 Font Family: Arial Font Style: normal Font Weight: normal Font Decoration: none
Description: The stream geomorphic assessment (SGA) is a physical assessment competed by geomorphologists to determine the condition and sensitivity of a stream. The SGA Reach Breaks are points that indicate where the Phase 1 SGA reach breaks are. They are based on changes in topography, slope and valley setting. Where there is a significant change in any of the above there is a reach break created.
Color: [255, 0, 0, 255] Background Color: N/A Outline Color: N/A Vertical Alignment: bottom Horizontal Alignment: center Right to Left: false Angle: 0 XOffset: 0 YOffset: 0 Size: 8 Font Family: Arial Font Style: normal Font Weight: normal Font Decoration: none
Description: The stream geomorphic assessment (SGA) is a physical assessment competed by geomorphologists to determine the condition and sensitivity of a stream. The Phase 2 SGA is the second phase of SGA data collection and is largely a field based data collection. The SGA Phase 2 Assessed Reaches indicates where the SGA Phase 2 has been completed in Vermont.
Description: The stream geomorphic assessment (SGA) is a physical assessment competed by geomorphologists to determine the condition and sensitivity of a stream. The Phase 1 SGA is the remote sensing first phase that gets completed largely in an office setting. The SGA Phase 1 Assessed Reaches indicates where the SGA Phase 1 has been completed in Vermont.
Description: The stream geomorphic assessment is a physical assessment competed by geomorphologists to determine the condition and sensitivity of a stream. The SGA locations shows the outermost watershed boundaries for our SGA projects.
Description: River corridors are delineated to provide for the least erosive meandering and floodplain geometry toward which a river will evolve over time. River corridor maps guide State actions to protect, restore, and maintain naturally stable meanders and riparian areas to minimize erosion hazards. Land within and immediately abutting a river corridor may be at higher risk to fluvial erosion during floods.
Copyright Text: Vermont River Corridor and Floodplain Protection Program
VT Dept of Environmental Conservation, ANR
Description: Section 303(d) of the federal Clean Water Act requires Vermont, every two years, to prepare a list of all surface waters in the state for which beneficial uses - such as for drinking, recreation, aquatic habitat, and industrial use - are impaired by pollutants. These are surface waters not expected to meet Vermont Water Quality Standards within a reasonable time even after best management practices are applied. All impaired surface waters listed require the development and implementation of a pollutant loading and reduction plan, or TMDL (Total Maximum Daily Load). The 2010 Clean Water Act Section 303(d) list, Vermont 303(d) List of Waters, has been prepared in accordance with the Vermont Surface Water Assessment and Listing Methodology, current EPA Guidance, and the Environmental Protection Regulations 40 CFR 130.7.
Description: Section 303(d) of the federal Clean Water Act requires Vermont, every two years, to prepare a list of all surface waters in the state for which beneficial uses - such as for drinking, recreation, aquatic habitat, and industrial use - are impaired by pollutants. These are surface waters not expected to meet Vermont Water Quality Standards within a reasonable time even after best management practices are applied. All impaired surface waters listed require the development and implementation of a pollutant loading and reduction plan, or TMDL (Total Maximum Daily Load). The 2010 Clean Water Act Section 303(d) list, Vermont 303(d) List of Waters, has been prepared in accordance with the Vermont Surface Water Assessment and Listing Methodology, current EPA Guidance, and the Environmental Protection Regulations 40 CFR 130.7.
Description: Section 303(d) of the federal Clean Water Act requires Vermont, every two years, to prepare a list of all surface waters in the state for which beneficial uses - such as for drinking, recreation, aquatic habitat, and industrial use - are impaired by pollutants. These are surface waters not expected to meet Vermont Water Quality Standards within a reasonable time even after best management practices are applied. All impaired surface waters listed require the development and implementation of a pollutant loading and reduction plan, or TMDL (Total Maximum Daily Load). The 2010 Clean Water Act Section 303(d) list, Vermont 303(d) List of Waters, has been prepared in accordance with the Vermont Surface Water Assessment and Listing Methodology, current EPA Guidance, and the Environmental Protection Regulations 40 CFR 130.7.
EventType
(
type: esriFieldTypeInteger, alias: EventType
, Coded Values:
[1: Part A (TMDL required)]
, [3: Part C (further assessment)]
, [7: Part G (channel alteration)]
, ...9 more...
)
TMDL_ID
(
type: esriFieldTypeInteger, alias: TMDL ID
)
Name: Small MS4 (Municipal Separate Storm Sewer Systems) Area
Display Field: Name
Type: Feature Layer
Geometry Type: esriGeometryPolygon
Description: The dataset contains the boundaries of the MS4 general permit, which are defined as the intersection of US Census urbanized areas and the watershed boundaries of the stormwater-impaired waters with approved TMDLs.
Description: Stormwater impaired watersheds occuring on both the Priority Waters (Part D - Completed TMDL) and 303(d) list of waters (Part A - need TMDL) The Vermont State Legislature has required the Agency of Natural Resources (ANR) to develop water quality remediation plans for each of the stormwater impaired waters listed on the year 2004 303(d) list of impaired waters. This effort, the Vermont Stormwater Project, is being executed by the Stormwater Management Section (SMS) of the Water Quality Division (WQD) using the "Stormwater Cleanup Plan Framework" publication as guidance in developing these remediation plans. The term "303(d)" refers to a section of the Federal Clean Water Act that requires all states to develop lists of impaired waters not meeting Water Quality Standards. The Federal Clean Water Act requires "Total Maximum Daily Loads" (TMDLs) to be developed for waters on the list along with a schedule for implementation. "A TMDL is the calculation of the maximum amount of a pollutant that a water body can receive and still meet Vermont Water Quality Standards. In a broader sense, a TMDL is a plan that identifies the pollutant reductions a water body needs to meet Vermont's Water Quality Standards and develops a means to implement those reductions."
Name: Wetland Restoration Model Site Prioritization (Lake Champlain 2017)
Display Field: Site_Group
Type: Feature Layer
Geometry Type: esriGeometryPolygon
Description: The State of Vermont, in partnership with 25 organizations, agencies, businesses and non-profits, received funding in 2015 from the U.S. Department of Agriculture’s Natural Resources Conservation Service (NRCS) through the Regional Conservation Partnership Program (RCPP). This $16 million grant was the second largest in the country and is helping landowners in the Lake Champlain Basin of Vermont and New York invest in best conservation practices to improve water quality. The Lake Champlain RCPP provides financial and technical assistance to agricultural and forest landowners to develop and implement site-specific farm and forest projects that will directly improve water quality in streams and rivers that flow towards Lake Champlain. The RCPP funds
will also help conserve important and environmentally critical agricultural lands, and restore and protect wetlands crucial to attenuating sediment and nutrients and slowing floodwaters. These funds are committed through 2020, but may be extended, or new sources made available, in the future.
The Wetland Restoration Model Site Prioritization Map (this layer) builds on a model initially developed in 2007 ranked potential wetland restoration sites based on various physical characteristics of an area. The intent of this layer is to identify land that has potential to be a priority for wetlands restoration.
Description: This dataset represents wetlands included in Vermont's Significant Wetlands Inventory (WaterWetlands_VSWI). Questions about wetland location and use should be referred to the ANR DEC Wetlands section, 802-244-6951. NWI maps were used by the State of Vermont Agency of Natural resources as a means of creating this data layer in conjunction with the VSWI. The NWI and VSWI were joined by a union, to create the new 2010 Vermont Significant Wetland Inventory data layer, representing Vermont's regulatory wetlands. The VSWI prior to 2010 was created by hand digitizing nearly two-thirds of Vermont's wetlands from RF 24000 scale NWI mylars. The remainder of the state was scanned from RF 24000 or RF 25000 scale mylars.These mylars were created by transfering wetland polygon boundaries from RF 62500 scale NWI mylars to RF 24000 scale base maps.
Description: The Wetland Advisory Layer is a supplemental wetland mapping layer. It does not carry the same regulatory weight as the Vermont Significant Wetland Inventory (VSWI) maps, but may provide better information on the size and configuration of wetlands in the landscape. There are multiple sources for the advisory layer, but this layer is not uniform across the state due to its origins.Regulatory Meaning: Where the advisory layer touches or overlaps with a VSWI layer, it is likely protected by the Vermont Wetland Rules (VWR). If the wetland meets the presumption of significance listed in Section 4.6 of the Vermont Wetland Rules, it would also be considered a Class II wetland. Any work in a Class I or II wetland or its jurisdictional buffer, including filling, dredging, draining, ditching, cutting woody vegetation, may require a permit from the Vermont Wetlands Program. Both Class I and Class II wetlands appear on the VSWI maps. Class II wetlands have a 50-foot buffer which is protected, and Class I wetlands have a 100-foot regulatory buffer. These buffers are measured from the edge of a delineated boundary (field verified) from the wetland.Origin: Wetland Advisory maps are a combination of wetland mapping created by towns, from Wetland Program site visits, or by advanced state mapping efforts. Where base maps originate from aerial photography, those imagery is more recent than National Wetland Inventory derived VSWI maps. Some advisory layers use LiDAR and have also had field verification, such as the pilot project that mapped the Missisquoi River Basin in 2019.
Description: The VT DEC (Vermont Department of Environmental Conservation) manages an inventory of lake and pond information. The "Lakes and Ponds Inventory" stores the Water Quality Division's survey and monitoring information used to determines water quality problems and ways to solve them.
Description: The VT DEC (Vermont Department of Environmental Conservation) manages an inventory of lake and pond information. The "Lakes and Ponds Inventory" stores the Watershed Management Division's survey and monitoring information used to determines water quality problems and ways to solve them. A project completed by ADS-ANR GIS staff delineated the watersheds and created a web mapping application that allows Lakes Program staff to review, edit, and upload new watershed boundaries for the 800+ lakes in the Lakes Inventory. The layer has editor tracking enabled and filters on “accepted” watersheds.
Copyright Text: Lakes and Ponds Management and Protection Program, ADS-ANR GIS
Description: Identification number, name and geographic description of the major river segments in Vermont according to the Water Body Identification system used to identify lakes, streams and major rivers in the state.
Description: Identification number, name and geographic description of the major river segments in Vermont according to the Water Body Identification system used to identify lakes, streams and major rivers in the state.
Description: Identification of watersheds associated with Waterbody Identification numbers as part of the Waterbody identification system for the State of Vermont
Color: [156, 156, 156, 255] Background Color: N/A Outline Color: N/A Vertical Alignment: bottom Horizontal Alignment: center Right to Left: false Angle: 0 XOffset: 0 YOffset: 0 Size: 12 Font Family: Arial Font Style: normal Font Weight: normal Font Decoration: none
Description: Vermont List of Priority Surface Waters outside CWA Section 303(d) is divided in to 4 parts, Parts B, D, E and F. The four-part list has managed by the Vermont Department of Environmental Conservation (VT DEC) in accordance with the Vermont Surface Water Assessment and Listing Methodology. Each part is considered to be outside the scope of Clean Water Act Section 303(d). PART B. IMPAIRED SURFACE WATERS - NO TOTAL MAXIMUM DAILY LOAD DETERMINATION REQUIRED - all waters listed in Part B are assessed as impaired and do not require development of a TMDL as described in 40 CFR 130.7. Section 303d of the Federal Clean Water Act does not govern these waters. Impaired waters that do not need a TMDL are those where other pollution control requirements (such as best management practices) required by local, state or federal authority are expected to address all water-pollutant combinations and the Water Quality Standards are expected to be attained in a reasonable period of time. These waters correspond to Category 4b of EPA's Consolidated Assessment Listing Methodology. PART D. SURFACE WATERS WITH COMPLETED AND APPROVED TMDLs - all waters identified on Part D have appeared on a previous version of the Part A-303d List and also have completed and approved TMDLs in place. If future assessments show the impairment has been eliminated, the waters will remain on Part D as a means of TMDL tracking, however, the current assessment status of the water will be noted. These waters correspond to Category 4a of EPA's Consolidated Assessment Listing Methodology. PART E. SURFACE WATERS ALTERED BY EXOTIC SPECIES - waters appearing in Part E are assessed as altered. They represent situations to be given priority for management where aquatic habitat and/or other designated uses have been altered to the extent that one or more designated uses are not supported due to the presence of exotic aquatic species. This list currently includes waters altered by the proliferation of Eurasian watermilfoil, water chestnut, zebra mussels or the presence of alewives. These waters correspond to Category 4c of EPA's Consolidated Assessment Listing Methodology. PART F. SURFACE WATERS ALTERED BY FLOW REGULATION - waters appearing in Part F of the Vermont Priority Waters List are assessed as altered. They represent priority management situations where aquatic habitat and/or other designated uses have been altered by flow regulation to the extent that one or more designated uses are not supported. Alterations arise from flow fluctuation, obstructions, or other manipulations of water levels that originate from hydroelectric facilities or other dam operations or from water withdrawals for industrial or municipal water supply or snowmaking purposes. These waters correspond to Category 4c of EPA's Consolidated Assessment Listing Methodology.
EventType
(
type: esriFieldTypeInteger, alias: EventType
, Coded Values:
[3: Part C (further assessment)]
, [7: Part G (channel alteration)]
, [1: Part A (needs TMDL)]
, ...8 more...
)
ID
(
type: esriFieldTypeString, alias: ID, length: 40
)
Description: Vermont List of Priority Surface Waters outside CWA Section 303(d) is divided in to 4 parts, Parts B, D, E and F. The four-part list has managed by the Vermont Department of Environmental Conservation (VT DEC) in accordance with the Vermont Surface Water Assessment and Listing Methodology. Each part is considered to be outside the scope of Clean Water Act Section 303(d). PART B. IMPAIRED SURFACE WATERS - NO TOTAL MAXIMUM DAILY LOAD DETERMINATION REQUIRED - all waters listed in Part B are assessed as impaired and do not require development of a TMDL as described in 40 CFR 130.7. Section 303d of the Federal Clean Water Act does not govern these waters. Impaired waters that do not need a TMDL are those where other pollution control requirements (such as best management practices) required by local, state or federal authority are expected to address all water-pollutant combinations and the Water Quality Standards are expected to be attained in a reasonable period of time. These waters correspond to Category 4b of EPA's Consolidated Assessment Listing Methodology. PART D. SURFACE WATERS WITH COMPLETED AND APPROVED TMDLs - all waters identified on Part D have appeared on a previous version of the Part A-303d List and also have completed and approved TMDLs in place. If future assessments show the impairment has been eliminated, the waters will remain on Part D as a means of TMDL tracking, however, the current assessment status of the water will be noted. These waters correspond to Category 4a of EPA's Consolidated Assessment Listing Methodology. PART E. SURFACE WATERS ALTERED BY EXOTIC SPECIES - waters appearing in Part E are assessed as altered. They represent situations to be given priority for management where aquatic habitat and/or other designated uses have been altered to the extent that one or more designated uses are not supported due to the presence of exotic aquatic species. This list currently includes waters altered by the proliferation of Eurasian watermilfoil, water chestnut, zebra mussels or the presence of alewives. These waters correspond to Category 4c of EPA's Consolidated Assessment Listing Methodology. PART F. SURFACE WATERS ALTERED BY FLOW REGULATION - waters appearing in Part F of the Vermont Priority Waters List are assessed as altered. They represent priority management situations where aquatic habitat and/or other designated uses have been altered by flow regulation to the extent that one or more designated uses are not supported. Alterations arise from flow fluctuation, obstructions, or other manipulations of water levels that originate from hydroelectric facilities or other dam operations or from water withdrawals for industrial or municipal water supply or snowmaking purposes. These waters correspond to Category 4c of EPA's Consolidated Assessment Listing Methodology.
EventType
(
type: esriFieldTypeInteger, alias: EventType
, Coded Values:
[1: Part A (TMDL required)]
, [3: Part C (further assessment)]
, [7: Part G (channel alteration)]
, ...9 more...
)
ID
(
type: esriFieldTypeString, alias: ID, length: 40
)
TMDL_ID
(
type: esriFieldTypeInteger, alias: TMDL ID
)
Part
(
type: esriFieldTypeString, alias: Part, length: 3
)
Description: The Vermont Water Quality Standards (VTWQS) are rules intended to achieve the goals of the Vermont Surface Water Strategy, as well as the objective of the federal Clean Water Act which is to restore and maintain the chemical, physical, and biological integrity of the Nation's water. The classification of waters is in included in the VTWQS. The classification of all waters has been established by a combination of legislative acts and by classification or reclassification decisions issued by the Water Resources Board or Secretary pursuant to 10 V.S.A. § 1253. Those waters reclassified by the Secretary to Class A(1), A(2), or B(1) for any use shall include all waters within the entire watershed of the reclassified waters unless expressly provided otherwise in the rule. All waters above 2,500 feet altitude, National Geodetic Vertical Datum, are designated Class A(1) for all uses, unless specifically designated Class A(2) for use as a public water source. All waters at or below 2,500 feet altitude, National Geodetic Vertical Datum, are designated Class B(2) for all uses, unless specifically designated as Class A(1), A(2), or B(1) for any use.
Copyright Text: Watershed Management Division, VT Department of Environmental Conservation
AquaticBiota
(
type: esriFieldTypeString, alias: Aquatic Biota, length: 10
, Coded Values:
[A1: Class A(1) Ecological Waters]
, [A2: Class A(2) Public Water Supplies]
, [B1: Class B(1) Other Waters]
, ...1 more...
)
AquaticHabitat
(
type: esriFieldTypeString, alias: Aquatic Habitat, length: 10
, Coded Values:
[A1: Class A(1) Ecological Waters]
, [A2: Class A(2) Public Water Supplies]
, [B1: Class B(1) Other Waters]
, ...1 more...
)
Aesthetic
(
type: esriFieldTypeString, alias: Aesthetic, length: 10
, Coded Values:
[A1: Class A(1) Ecological Waters]
, [A2: Class A(2) Public Water Supplies]
, [B1: Class B(1) Other Waters]
, ...1 more...
)
Boating
(
type: esriFieldTypeString, alias: Boating, length: 10
, Coded Values:
[A1: Class A(1) Ecological Waters]
, [A2: Class A(2) Public Water Supplies]
, [B1: Class B(1) Other Waters]
, ...1 more...
)
Fishing
(
type: esriFieldTypeString, alias: Fishing, length: 10
, Coded Values:
[A1: Class A(1) Ecological Waters]
, [A2: Class A(2) Public Water Supplies]
, [B1: Class B(1) Other Waters]
, ...1 more...
)
Swimming
(
type: esriFieldTypeString, alias: Swimming, length: 10
, Coded Values:
[A1: Class A(1) Ecological Waters]
, [A2: Class A(2) Public Water Supplies]
, [B1: Class B(1) Other Waters]
, ...1 more...
)
PublicWater
(
type: esriFieldTypeString, alias: Public Water Source, length: 10
, Coded Values:
[A1: Class A(1) Ecological Waters]
, [A2: Class A(2) Public Water Supplies]
, [B1: Class B(1) Other Waters]
, ...1 more...
)
Irrigation
(
type: esriFieldTypeString, alias: Irrigation, length: 10
, Coded Values:
[A1: Class A(1) Ecological Waters]
, [A2: Class A(2) Public Water Supplies]
, [B1: Class B(1) Other Waters]
, ...1 more...
)