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These points were created to better represent spatially the locations of actual visual encounters, instead of just the survey routes (HVESSampleLines). This point file will be used for analysis - to buffer and intersect with various landscape features.<\/SPAN><\/P>

Since 2006, staff have conducted visual encounter survey (VES) to assess amphibian distribution and abundance. OSMP staff monitor wetlands for the presence of native amphibians with a focus on locating sites that support northern leopard frogs (Lithobates pipiens)\u2014a state sensitive species and one that staff specifically manage for as outlined in the Grassland Ecosystem Management Plan (Grassland Plan). 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Study routes for amphibian visual encounters survey. Routes are next to streams and pond/lake perimeters.<\/SPAN><\/P>

Since 2006, staff have conducted visual encounter surveys in one form or another (VES) to assess amphibian distribution and abundance. OSMP staff monitor wetlands for the presence of native amphibians with a focus on locating sites that support northern leopard frogs (Lithobates pipiens)\u2014a state sensitive species and one that staff specifically manage for as outlined in the Grassland Ecosystem Management Plan (Grassland Plan). 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THIS DATASET IS CONSIDERED SENSITIVE; PLEASE CONSULT WILDLIFE STAFF FOR GUIDANCE PRIOR TO ITS USE.<\/SPAN><\/P>

This feature class contains all point features representing the on the ground points related to transected for Grassland Bird Monitoring. It inludes origin, middle and endpoints. This transect monitoring protocol is now used system-wide within OSMP grasslands. This contains transects were made during the grassland planning process to monitor grassland birds systemwide as well as original transects that were created before the grassland plan; design usually associated with Trails Study Area plans. If transects are added or modified by biologists, data is provided to GIS staff to update in this database. 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THIS DATASET IS CONSIDERED SENSITIVE; PLEASE CONSULT WILDLIFE STAFF FOR GUIDANCE PRIOR TO ITS USE.<\/SPAN><\/P>

This feature class contains all line features representing the on the ground path to be transected for Grassland Bird Monitoring. This transect monitoring protocol is now used system-wide within OSMP grasslands. This contains transects were made during the grassland planning process to monitor grassland birds systemwide as well as original transects that were created before the grassland plan; design usually associated with Trails Study Area plans. 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Forest raptor monitoring points updated for the WTSA process. Includes call points for Forest Owls and Forest Hawks. Target species are northern goshawk and flammulated owls. Detailed list of point names is listed in supplemental Info. 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To monitor the effects of new trail development on ungulate use of the areas<\/SPAN><\/SPAN>, OSMP staff designed a monitoring plan that included the creation of pellet plots near the Spring Brook Loop and Goshawk Ridge Trails. Staff collected data one year prior to trail construction, and then once annually since the completion of the trail in 2008. Pellet plots consist of a center pivot point for a 5 m radius circular plot. Each plot is systematically searched for animal scat, with a focus on large ungulates, carnivores, and wild turkey. Staff randomly placed the plots at varying distances from the trails (i.e., treatment) and included 25 plots in an untrailed area to act as a control. The Goshawk Ridge Trail plots are separated even more intricately with plots stratified into seven different distance classes: 0-50m, 50-100m, 100-150m, 150-200m, 200-250m, 250-300m, and Controls. The project draws assistance from many different staff members, being organized and anchored by the Wildlife Crew, but being assisted by the Forestry, Trails, IMP, and Restoration Crews. In the early years, this project was part of an All Staff Work Day effort, but in recent years we have reverted to using smaller crews of more experienced people.<\/SPAN><\/SPAN><\/P>

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The Preble's meadow jumping mouse (Preble's or PMJM) is a small mammal approximately 9 inches in length with large hind feet adapted for jumping, a long bicolored tail (which accounts for 60% of its length), and a distinct dark stripe down the middle of its back which is bordered on either side by gray to orange-brown fur. To evade predators, the mouse can jump up to three feet. The species historical range included Colorado, Wyoming.<\/SPAN><\/P>

This dataset identifies Preble's Meadow Jumping Mouse critical habitat areas on City of Boulder Open Space and Mountain Parks lands. Critical habitat is a term defined and used in the Endangered Species Act. 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This data tracks the spatial extent of black-tailed prairie dog colonies on OSMP-managed lands over time, including any held in fee and on conservation easements where the department has a management agreement in place.<\/SPAN><\/P>

Data was collected using GPS and clipped to the City of Boulder Open Space and Mountain Parks (OSMP) and Boulder County Parks and Open Space (BCPOS) properties. It has been collected yearly each fall since 1996, by OSMP wildlife staff. <\/SPAN><\/P>

Black-tailed prairie dog colonies create a unique habitat on the landscape. They create habitat and food for other animals of federal, state, and local conservation concern (e.g. burrowing owls, ferruginous hawks, bald and golden eagles, American badger, etc., (see the OSMP Grassland Ecosystem Management Plan for more details)). Their burrowing activity also causes conflicts when it occurs on parcels where the management focus is on agriculture or other purposes. The conflict can be especially high in areas of irrigated grasslands since the burrowing activity can alter how water is applied to the landscape, and prairie dog browsing can remove graminoid cover and encourage invasions of tenacious non-native form species. <\/SPAN><\/P>

System-wide mapping was first initiated by the mandate to monitor black-tailed prairie dogs in the \u201cCity of Boulder Grassland Management: Black-tailed Prairie Dog Habitat Conservation Plan\u201d. This plan was approved by the City of Boulder Open Space Board of Trustees on March 13, 1996. Annual system-wide mapping began that fall, and continued each subsequent fall starting on Sept 1. In 2012 a field was added to distinguish active vs inactive colonies. At this time we began also collecting inactive colony boundaries.<\/SPAN><\/P>

The spatial data informs the public, lessees, academic researchers, and partnering agencies as to the extent of the black-tailed prairie dogs on our properties. This data informs conservation planning for sensitive species, including the federally endangered black-footed ferret. The annual mapping can be used to visually demonstrate how populations fluctuate, highlight areas of conflict, and inform management decisions. This long term data set allows for a retrospective view of where prairie dogs have occurred on the system in the past, but where they may no longer persist. This historic view helps staff identify areas where prairie dogs are likely to become reestablished, either through natural recolonization or by direct relocation. Information on where prairie dogs have or do exist also helps inform Habitat Suitability Models. The data set also provides staff with tools to make management decision based on colony management designations (Prairie Dog Conservation Area, Grassland Preserve, Multiple Objective Area, Transition Area, Removal Area (see OSMP Grassland Ecosystem Management Plan for specifics on the designation process)) <\/SPAN><\/P>

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This dataset contains field mapped perimeters of all active prairie dog colonies. Data was collected using GPS and clipped to the City of Boulder Open Space and Mountain Parks (OSMP) and Boulder County Parks and Open Space (BCPOS) properties. It has been collected yearly each fall since 1996, by OSMP wildlife staff.<\/SPAN><\/P>

The data set also provides prairie dog colony management designations (Prairie Dog Conservation Area, Grassland Preserve, Multiple Objective Area, Transition Area, Removal Area (see <\/SPAN>OSMP Grassland Ecosystem Management Plan <\/SPAN><\/A>for specifics on the designation process)) <\/SPAN><\/P>

Prairie dog colony management designations:<\/SPAN><\/P>

Grassland Preserve<\/SPAN>: Conservation of prairie dogs and their associated species in large and ecologically diverse grassland habitat blocks.<\/SPAN><\/P>

Multiple Objective Areas<\/SPAN>: Conservation of prairie dogs and their associated species is one of multiple management objectives.<\/SPAN><\/P>

Prairie Dog Conservation Areas<\/SPAN>: Conservation of the prairie dog is the primary management objective; associated species managed opportunistically<\/SPAN><\/P>

Transition Areas<\/SPAN>: Conservation of targets other than the prairie dog and associated community takes precedence-removal generally when relocation sites are available<\/SPAN><\/P>

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THIS DATASET IS CONSIDERED SENSITIVE; PLEASE CONSULT WILDLIFE STAFF FOR GUIDANCE PRIOR TO ITS USE.<\/SPAN><\/P>

This dataset includes all known Accipiter nests on OSMP Lands (includees Northern Goshawk, Sharp-Shinned Hawk and Cooper's Hawk). Data initially was collected around 2005 using systemwide call-back survey. Now biologists focus on known territories for annual surveys. Locations of nest trees are captured with Garmin GPS Units. 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The ForestMonitoringPlots dataset includes all vegetation sampling that has been done in OSMP forests. The monitoring and inventory projects represented here are- forest overstory walk-throughs, forest overstory inventories, Open space forest understory monitoring, and long-term understory modified whittaker plots. All of the raw data collected at these points is stored in the OSMP Monitoring database or the OSMP Forest Inv Database. <\/SPAN><\/P>

Attributes include the type of inventory, the associated forest stand, the type of plot (overstory/understroy), the plot name, the old open space stand name if it applies, and how the point was recorded (GPS, digitized, etc). The points in the dataset may be adjusted over time as digitized points are replaced by GPS data. 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The GMAP Long Term Monitoring Transects are the transects used to evaluate various indicators of non-wetland grassland (xeric tallgrass prairie, mixedgrass prairie mosiac, and mesic bluestem prairie) condition. There are 96 transects in mixedgrass prairie habitat, 44 transects in xeric tallgrass prairie, and 20 transects in mesic bluestem prairie for a total of 160 transects. The transect locations were established using a GRTS sampling design run in the statistical software package R. We used a stratified sampling design (stratified by habitat/target type - xeric tallgrass prairie, mixedgrass prairie mosiac, and mesic bluestem prairie) and transects were assigned by the GRTS process to one of four panels. The GRTS sampling design provides randomly selected, spatially balanced transect locations to ensure coverage of the entire study area. 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Measures the height and abundance of tall oatgrass and the cover of all vascular species and ground cover before and after cattle grazing in 40 grazed and ungrazed (caged) plots.<\/SPAN><\/P>

Tall oatgrass is a non-native grass species that is invading upland grasslands at a rapid pace. We have uncertainty on how to best manage the species and how management such as intensive grazing, which was implemented in 2015 influences native vegetation and tall oatgrass abundance in the long-term. This study examines the efficacy of grazing as a management tool in the containment zone.<\/SPAN><\/P><\/DIV><\/DIV><\/DIV>", "geometryType": "esriGeometryPoint", "sourceSpatialReference": { "wkid": 2876, "latestWkid": 2876, "xyTolerance": 0.003280833333333333, "zTolerance": 0.001, "mTolerance": 0.001, "falseX": -118265500, "falseY": -95180100, "xyUnits": 3048.006096012192, "falseZ": 0, "zUnits": 1, "falseM": 0, "mUnits": 1 }, "copyrightText": "", "parentLayer": { "id": 10, "name": "Vegetation Monitoring Locations" }, "subLayers": [], "minScale": 0, "maxScale": 0, "referenceScale": 0.0, "drawingInfo": { "renderer": { "type": "simple", "symbol": { "type": "esriSMS", "style": "esriSMSCircle", "color": [ 50, 0, 158, 255 ], "size": 4, "angle": 0, "xoffset": 0, "yoffset": 0, "outline": { "color": [ 0, 0, 0, 255 ], "width": 1 } } }, "scaleSymbols": true, "transparency": 0, "labelingInfo": null }, "defaultVisibility": true, "extent": { "xmin": 3062133.014852345, "ymin": 1231105.465917334, "xmax": 3063336.4304245114, "ymax": 1232468.8017733395, "spatialReference": { "wkid": 2876, "latestWkid": 2876, "xyTolerance": 0.003280833333333333, "zTolerance": 2, "mTolerance": 0.001, "falseX": -118265500, "falseY": -95180100, "xyUnits": 3.7138342128391795E7, "falseZ": 0, "zUnits": 1, "falseM": -100000, "mUnits": 10000 } }, "hasAttachments": false, "htmlPopupType": "esriServerHTMLPopupTypeAsHTMLText", "displayField": "SampleName", "typeIdField": null, "subtypeFieldName": null, "subtypeField": null, "defaultSubtypeCode": null, "fields": [ { "name": "OBJECTID", "type": "esriFieldTypeOID", "alias": "OBJECTID", "domain": null }, { "name": "SampleName", "type": "esriFieldTypeString", "alias": "SampleName", "length": 32, "domain": null }, { "name": "PlotType", "type": "esriFieldTypeString", "alias": "PlotType", "length": 4, "domain": null }, { "name": "MapPoints", "type": "esriFieldTypeString", "alias": "MapPoints", "length": 20, "domain": null }, { "name": "SampleID", "type": "esriFieldTypeInteger", "alias": "SampleID", "domain": null }, { "name": "Shape", "type": "esriFieldTypeGeometry", "alias": "Shape", "domain": null } ], "geometryField": { "name": "Shape", "type": "esriFieldTypeGeometry", "alias": "Shape" }, "indexes": [ { "name": "R153_pk", "fields": "OBJECTID", "isAscending": true, "isUnique": true, "description": "" }, { "name": "S139_idx", "fields": "Shape", "isAscending": true, "isUnique": true, "description": "" } ], "subtypes": [], "relationships": [], "canModifyLayer": false, "canScaleSymbols": false, "hasLabels": false, "capabilities": "Map,Query,Data", "maxRecordCount": 1000, "supportsStatistics": true, "supportsExceedsLimitStatistics": true, "supportsAdvancedQueries": true, "supportedQueryFormats": "JSON, geoJSON, PBF", "isDataVersioned": false, "ownershipBasedAccessControlForFeatures": {"allowOthersToQuery": true}, "useStandardizedQueries": true, "supportedSpatialRelationships": [ "esriSpatialRelIntersects", "esriSpatialRelContains", "esriSpatialRelCrosses", "esriSpatialRelEnvelopeIntersects", "esriSpatialRelIndexIntersects", "esriSpatialRelOverlaps", "esriSpatialRelTouches", "esriSpatialRelWithin", "esriSpatialRelRelation" ], "advancedQueryCapabilities": { "useStandardizedQueries": true, "supportsStatistics": true, "supportsPercentileStatistics": true, "supportsHavingClause": true, "supportsOrderBy": true, "supportsDistinct": true, "supportsCountDistinct": true, "supportsPagination": true, "supportsLod": false, "supportsQueryWithLodSR": false, "supportsTrueCurve": true, "supportsQueryWithDatumTransformation": true, "supportsReturningQueryExtent": true, "supportsQueryWithDistance": true, "supportsSqlExpression": true, "supportsTimeRelation": true, "supportsSqlFormat": false, "supportsQueryAnalytic": true }, "supportsDatumTransformation": true, "advancedQueryAnalyticCapabilities": { "supportsLinearRegression": true, "supportsAsync": false, "supportsPercentileAnalytic": true }, "dateFieldsTimeReference": null, "preferredTimeReference": null, "datesInUnknownTimezone": false, "hasMetadata": true, "isDataArchived": false, "archivingInfo": { "supportsQueryWithHistoricMoment": false, "startArchivingMoment": -1 }, "supportsCoordinatesQuantization": true, "supportsDynamicLegends": true }, { "currentVersion": 10.91, "cimVersion": "2.9.0", "id": 13, "name": "TGW Vegetation Monitoring", "type": "Feature Layer", "description": "

Vegetation monitoring in the Tallgrass West Implementation area tracks species composition, structure, and diversity of ~900 acres of grassland in the 1370-acre Tall Grass West Implementation Area, an important transitional area between the Rocky Mountain foothills and the Western Great Plains. The purpose of the monitoring is to describe the species composition, structure and diversity of the grassland vegetation, to determine temporal changes over time, and to relate those changes to agricultural management practices. <\/SPAN><\/P>

<\/P>

26 permanent monitoring transects were installed in 2005 in the Boulder Greens Venture, Dover-Blacker, Hedgecock, Stengel I, T.H.P., Frasier Farms and Wells east properties. The area was stratified by three grazing treatments (continuously grazed, ungrazed since 2006, and ungrazed for > 10 years prior to 2006) and environmental gradient (riparian/floodplain, upland terraces, and grassland-forest inteface) and transects were randomly placed within each stratum where possible. 15 of the 26 vegetation transects were aligned with wildlife transects established at the same time to characterize bird habitat near and far from trails: random locations were constrained to areas near these transects. Additional transects established by ESCO Associates in earlier years as part of the Tall Grass State Natural Area Monitoring (10 transects) and Prairie Dog Vegetation Monitoring (2 transects) were also sampled as part of this study.<\/SPAN><\/P>

<\/P>

Monitoring occurred in July or August between 2005 and 2008 with most but not all transects were sampled in all four years. Details about the sampling design, monitoring objectives and field procedures can be found in the project protocol. <\/SPAN><\/P>

<\/P>

The 50-m transects were oriented randomly from the origin point. The transect origins were marked in the field with rebar stakes driven flush with the ground and topped with labelled aluminum caps. Four-foot tall, white fiberglass stakes were positioned at both the origin and endpoint of each transect. Transect orientations were recorded to facilitate consistent relocation of the transects. Names in the feature class are a concatenation of the \u201cTGWV\u201d prefix for Tall Grass West Vegetation, followed by the transect number (1-33, but no transects numbered 4, 12, 15, 17, 20, 21, 23, 27, 31). The same name is used in the OSMP Inventory and Monitoring database, but a leading zero is added to the transect number.<\/SPAN><\/P>

Vegetation abundance was monitored by point-intercept technique using a point-projection device mounted on a tripod. Crosshairs visible in the eyepiece delineated the intercept point, and low magnification of the lens allowed the botanist to identify the species or substrate (i.e. bare soil, litter, rock) beneath the point. Second hits were recorded when the cover-point optical device intercepted an additional point of canopy vegetation directly beneath the 1st intercept reading. Point intercepts were taken on both sides of the transect at 1.0 m intervals along a 50-m transect to give 100 points per transect used to derive % cover by species. All species observed within a 2-m wide belt transect on both sides of the 50m transect were also listed with 0.1 cover to derive species richness. Transect were photographed during each monitoring session, looking from the origin to the end point.<\/SPAN><\/P>

Frequency data were collected in ten 1 m x 5 m subplots located on one side of the 50 m transect when looking from origin to endpoint. All species in the subplots were tallied and frequency was determined as the number of subplots in which the species was present divided by 10 total plots surveyed. While cover and species richness were consistently sampled, frequency was monitored in only a subset of plots in each year. <\/SPAN><\/P>

Additional details on study objectives, design and methods can be found in the Tallgrass West Vegetation Monitoring Project protocol, updated april 2013.<\/SPAN><\/P>

<\/P>

<\/P>

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Monitoring efforts include: <\/SPAN><\/P>