20190214
12061000
1.0
FGDC CSDGM Metadata
FALSE
20241115
13283600
150000000
5000
FGDC
IrrigatedLands_2016
002
0.000
2391980.200600
2740864.524400
1199411.123400
1519765.119100
1
file://\\dwrboifsvp03\GISData\Spatial\LandCover_Vegetation\SnakePlain\ESPA_IrrigatedLands\IrrigatedLands.gdb
Local Area Network
Projected
GCS_North_American_1983
Linear Unit: Meter (1.000000)
NAD_1983_Idaho_TM
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CalculateField IrrigatedLands_2016 ACRES "[Shape_Area] *0.0002471044" VB #
20241115
13283600
Geospatial Technology Section
Idaho Department of Water Resources
GIS
Geospatial Technology Section
322 East Front Street
Boise
Idaho
83720
gisinfo@idwr.idaho.gov
(208) 287-4800
(208) 287-6700
8:00 AM - 5:00 PM
Environment
Groundwater
Human
Hydrology
IDWR GIS Department
Irrigated Areas
Irrigation
Monitoring
Non-Irrigated
Regulatory
Semi-Irrigated
Surface Water
Water
Water Use
>
Eastern Snake Plain Aquifer, ESPA
Idaho, ID
>
Eastern Snake Plain Aquifer
ESPA
Environment
Groundwater
Human
Hydrology
IDWR GIS Department
Idaho
ID
Irrigated Areas
Irrigation
Monitoring
Non-Irrigated
Regulatory
Semi-Irrigated
Surface Water
Water
Water Use
Geospatial Technology Section
Idaho Department of Water Resources
GIS
Geospatial Technology Section
Idaho Department of Water Resources (IDWR)
<div style='text-align:Left;'><div><div><p><span>Access and Use Constraint: The Idaho Department of Water Resources is making this data available as a public service. The Idaho Department of Water Resources strives to ensure that all technical data and other information made available to the public is accurate, complete and in conformance with the Idaho Public Records Act. Neither the Department of Water Resources nor the State of Idaho, however, assumes any legal responsibility for the accuracy or completeness of the information contained on this site. Persons using information from this site for official purposes, or other purposes, for which accuracy and completeness are required, are hereby notified that they should first verify the information with the public records or other primary sources from which the information was obtained.</span></p><p><span>Please check sources, scale, accuracy, currentness and other available information. Please confirm that you are using the most recent copy of both data and metadata. Acknowledgement of IDWR in any products derived from this dataset is appreciated.</span></p></div></div></div>
Distribution Liability: The Idaho Department of Water Resources is making this data available as a public service. The Idaho Department of Water Resources strives to ensure that all technical data and other information made available to the public is accurate, complete and in conformance with the Idaho Public Records Act. Neither the Department of Water Resources nor the State of Idaho, however, assumes any legal responsibility for the accuracy or completeness of the information contained on this site. Persons using information from this site for official purposes, or other purposes, for which accuracy and completeness are required, are hereby notified that they should first verify the information with the public records or other primary sources from which the information was obtained. Acknowledgment of IDWR would be appreciated in any work derived from this dataset.
Field boundaries depicted within this dataset are not to be used for legal purposes.
2016 Irrigated Lands for the Eastern Snake Plain Aquifer: Hand-Digitized Generated
Geospatial Technology Section
Idaho Department of Water Resources
GIS
Geospatial Technology Section
322 East Front Street
Boise
Idaho
83720
gisinfo@idwr.idaho.gov
US
(208) 287-4800
(208) 287-6700
8:00 AM - 5:00 PM
Geospatial Technology Section
2021-06-03T00:00:00
2021-06-03T00:00:00
First Edition
Irrigated Lands for the ESPA
2016
20210603
Version 6.2 (Build 9200) ; Esri ArcGIS 10.9.1.28388
This dataset was generated for use in the calculation of recharge and evapotranspiration in order to calibrate the Eastern Snake Plain Aquifer Hydrologic Model.
<div style='text-align:Left;'><div><div><p><span>This layer depicts polygons representing land within the ESPA boundary classified as either "irrigated", "non-irrigated" or "semi-irrigated", where the semi-irrigated classification typically depicts residential land. </span></p><p><span>The creation of this dataset is a multi-year effort. The original line work that was used as a basis to create this dataset, is the Farm Service Agency’s (FSA) 2006 Common Land Unit (CLU) dataset, which is the most recent year the FSA distributed this data to the public. Project time constraints during the development of this dataset required acceptance of "less-than-perfectly-accurate" line work. In essence, line work deemed "close enough" to ground truth is acceptable for Eastern Snake Plain Aquifer (ESPA) modeling purposes. Field boundaries were then further refined using National Agriculture Imagery Program (NAIP) imagery, Digital Ortho Photo Quadrangle (DOQQ) imagery, or other high resolution imagery. </span></p><p><span>Attribute assignments for irrigation status (irrigated, non-irrigated, and semi-irrigated) are determined using available Landsat imagery as background reference. Landsat imagery is typically 30-meter (Landsat5) or 15-meter (Landsat7) resolution. National Agriculture Inventory Program (NAIP) imagery, Digital Ortho Photo Quadrangle (DOQQ) imagery, and other in-house, scanned aerial imagery is used for determining irrigation status and refining the polygon geometry. The interpretation and classification process is described in detail in the report, "2006 Irrigated Land Classification for the Eastern Snake Plain Aquifer" archived on the IDWR website: Legal Actions > Delivery Call Actions > SWC > Archived Matters > Technical Working Group Documents (https://idwr.idaho.gov/legal-actions/delivery-call-actions/SWC/archived-matters.html#twg-documents)</span></p><p><span>While data accuracy is highest inside the Eastern Snake Plain Aquifer Model boundary (ESPAM version 2), the layer does extend beyond the ESPAM2 boundary.</span></p></div></div></div>
10000
Irrigation status for the 2016 growing season.
-115.311656
-110.952490
41.957893
44.879291
2016-05-01T00:00:00
2016-11-30T00:00:00
1
-115.367480
-110.952490
44.879291
41.957893
Geospatial Technology Section
Idaho Department of Water Resources
GIS
Geospatial Technology Section
322 East Front Street
Boise
Idaho
83720
gisinfo@idwr.idaho.gov
(208) 287-4800
(208) 287-6700
8:00 AM - 5:00 PM
2011-01-01T00:00:00
2011-12-31T00:00:00
https://data-idwr.opendata.arcgis.com/pages/gis-data#IrrigatedLands
0.000
File Geodatabase Feature Class
ArcGIS Desktop 10.6.1
dataset
EPSG
9.5.1(10.8.0)
339484
Simple
FALSE
339484
TRUE
FALSE
Irrigated Lands Attribute Information
Feature Class
339484
3-class classification
IDWR
OBJECTID
OBJECTID
OID
4
0
0
Internal feature number.
Esri
Sequential unique whole numbers that are automatically generated.
Shape
Shape
Geometry
0
0
0
Feature geometry.
Esri
Coordinates defining the features.
ACRES
ACRES
Number of acres contained in the the polygon. This is user calculated and not updated automatically.
IDWR
Double
8
0
0
STATUS_2016
STATUS_2016
String
50
0
0
Irrigation status in 2016.
Values are either “irrigated”, “non-irrigated”, or “semi-irrigated”.
IDWR
20160501
20161130
irrigated
Area shows evidence of being irrigated
IDWR
non-irrigated
Area shows no evidence of being irrigated
IDWR
semi-irrigated
Residential area
IDWR
Shape_Length
Shape_Length
Double
8
0
0
Length of feature in internal units.
Esri
Positive real numbers that are automatically generated.
Shape_Area
Shape_Area
Double
8
0
0
Area of feature in internal units squared.
Esri
Positive real numbers that are automatically generated.
20241115
Irrigation status is determined using 2016 Landsat imagery for the following dates:
Path38Row30: 06-01, 06-17, 07-19, 08-04, 08-20, 09-05, 09-21, 10-07, 10-23 and
Path38Row31: 05-16 and
Path39Row29: 05-07, 05-23, 06-08, 06-24, 07-19, 07-26, 08-11, 08-27, 09-12, 09-28 and
Path39Row30: 05-07, 05-23, 06-08, 06-24, 07-26, 08-11, 08-27, 09-12, 09-28, 10-14 and
Path39Row31: 05-07, 05-23, 06-08, 06-24, 07-26, 08-11, 08-27, 09-12, 09-28 and
Path40Row29: 05-14, 05-30, 07-01, 08-02, 08-18, 09-03, 09-19, 10-05, 10-21 and
Path40Row30: 05-14, 05-30, 07-01, 08-02, 08-18, 09-03, 09-19, 10-05, 10-21 and
Path40Row31: 05-14, 05-30, 07-01, 08-02, 08-18, 09-03, 09-19, 10-05, 10-21 and
Path41Row28: 05-05, 06-06, 06-22, 07-08, 07-24, 08-09, 08-25, 09-10, 09-26 and
Path41Row29: 05-21, 06-06, 06-22, 07-08, 07-24, 08-09, 08-25, 09-10, 09-26, 10-12 and
Path41Row30: 05-05, 05-21, 06-06, 06-22, 07-08, 07-24, 08-09, 08-25, 09-10, 09-26, 10-12 and
Path41Row31: 05-05, 05-21, 06-06, 06-22, 07-08, 07-24, 08-09, 08-25, 09-10, 09-26, 10-12
AND
Irrigation status is determined using 2016 Sentinel2 imagery for the following tiles and dates:
T11TQG/T11TQH/T12TTM/T12TUM/T12TUN: 06-03, 05-11, 05-23, 05-29, 06-05, 06-08, 06-18, 06-25, 06-28, 07-02, 07-08, 07-15, 07-18, 08-07, 08-11, 08-17, 08-24, 08-27, 09-06, 09-26, 10-03, 10-06, 10-10, 10-16, 10-26, 11-05, 11-12, 11-15, 11-22
The creation of this dataset is a multi-year effort. Original linework is from the Farm Service Agency's (FSA) Common Land Unit (CLU) datasets of or around 2006 or 2014. FSA no longer distributes this data to the public. Project time constraints require acceptance of "less-than-perfectly-accurate" linework. In essence, line work deemed "close enough" to ground truth is acceptable for Eastern Snake Plain Aquifer (ESPA) modeling purposes. Attribute assignments for irrigation status (irrigated, non-irrigated, and semi-irrigated) are determined using available Landsat imagery as background reference. Landsat imagery is typically 30-meter (l5) resolution. National Agriculture Inventory Program (NAIP) imagery, Digital Ortho Photo Quadrangle (DOQQ) imagery, and other in-house, scanned aerial imagery is used for determining irrigation status and refining linework geometry. This dataset extends beyond the Eastern Snake Plain Aquifer Model boundary (ESPAM2). Line and attribute correctness is more accurate within ESPAM2 boundary.
2021-06-03T00:00:00
"Irrigated Lands" data was created from the best available data for each year.
"Irrigated Lands" data as provided by IDWR does not represent an on-the-ground survey nor is it based on a thorough water right review.
Irrigation status in the "Irrigated Lands" data is not determined using spectral signatures but is based on a GIS analyst's manual interpretation of remotely sensed imagery.
Field boundaries depicted within this dataset are not to be used for legal purposes.
The constantly expanding scope, completeness, and complexity of GIS technologies, including image processing and interpretation, allows IDWR to constantly improve upon the methodology used to create "Irrigated Lands" data. If you are interested in the evolution of the “Irrigated Lands” project, please contact IDWR’s GISInfo to obtain the Editing Methodology and Guidelines documentation.
Check Geometry Tool
Repair Geometry Tool
Check Topology: Correct overlapping polygon topology errors
*note: slightly overlapping polygons and gaps still exist, typically along pivot edges and/or roads
1) No Overlaps
2) No Gaps (*of significant size)
2021-06-03T00:00:00
"Irrigated Lands" data was created from the best available data for each year.
"Irrigated Lands" data as provided by IDWR does not represent an on-the-ground survey nor is it based on a thorough water right review.
Irrigation status in the "Irrigated Lands" data is not determined using spectral signatures but is based on a GIS analyst's manual interpretation of remotely sensed imagery.
Field boundaries depicted within this dataset are not to be used for legal purposes.
The constantly expanding scope, completeness, and complexity of GIS technologies, including image processing and interpretation, allows IDWR to constantly improve upon the methodology used to create "Irrigated Lands" data. If you are interested in the evolution of the “Irrigated Lands” project, please contact IDWR’s GISInfo to obtain the Editing Methodology and Guidelines documentation.
Positional Accuracy requirements are determined by its use in the ESPA modelling process which accepts "less-than-perfectly accurate" horizontal accuracy. However, given any time constraints, efforts are made to refine positional accuracy based on NAIP and DOQQ imagery.
Visual inspection against imagery and IDWR's water rights database.
Attribute assignments for irrigation status (irrigated, non-irrigated, and semi-irrigated) are determined using available Landsat and Sentinel2 satellite imagery as background reference. Landsat imagery is typically 30-meter (l5) or 15-meter (l7) resolution, Sentinel2 imagery is 10-meter resolution. National Agriculture Inventory Program (NAIP) imagery, Digital Ortho Photo Quadrangle (DOQQ) imagery, and other in-house, scanned aerial imagery is used for determining irrigation status and refining linework geometry. Hence, attribute accuracy is determined by the scale of those sources.
Visual inspection against imagery and IDWR's water rights database. A topology check was performed to repair overlapping polygons and data gaps of consequential size. Overlapping polygons and data gaps of consequential size were minimized to the best of the analyst’s ability under existing time constraints.
The data layer consists of polygon features attributed by GIS analysts based on visual interpretation of remote sensing and aerial imagery as well as supplemental information provided in the water rights database.
Attribute assignments for irrigation status (irrigated, non-irrigated, and semi-irrigated) are determined using available Landsat and Sentinel2 satellite imagery as background reference. Landsat imagery is typically 30-meter (l5) or 15-meter (l7) resolution, Sentinel2 imagery is 10-meter resolution. National Agriculture Inventory Program (NAIP) imagery, Digital Ortho Photo Quadrangle (DOQQ) imagery, and other in-house, scanned aerial imagery is used for determining irrigation status and refining linework geometry.
Concentrated animal feeding operations are classified as semi-irrigated in the 2011 and later Irrigated Lands Data layers.
Visual inspection against imagery and IDWR's water rights database.
While data accuracy and completeness is highest inside the Eastern Snake Plain Aquifer Model boundary (ESPAM version 2), the layer does extend beyond the ESPAM2 boundary and may or may not extend to any particular county line.
Visual inspection against imagery.
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