20150513 08443100 FALSE 20230602 10451400 20230602 10451400 ofpbds_pt 002 229230.392397 2319399.670732 88731.402753 1654661.696807 1 file://\\fwhqd2\Fish\Fish Share\GIS\FishPassageBarrierInventory\Publication\GDB\ofpbds_gdb.gdb Local Area Network ofpbds_gdb.GIS.ofpbds_pt__ATTACHREL Relationship ofpbds_gdb.GIS.ofpbds_pt__ATTACHREL Relationship Projected GCS_North_American_1983 NAD_1983_Oregon_Statewide_Lambert_Feet_Intl <ProjectedCoordinateSystem xsi:type='typens:ProjectedCoordinateSystem' xmlns:xsi='http://www.w3.org/2001/XMLSchema-instance' xmlns:xs='http://www.w3.org/2001/XMLSchema' xmlns:typens='http://www.esri.com/schemas/ArcGIS/10.7'><WKT>PROJCS[&quot;NAD_1983_Oregon_Statewide_Lambert_Feet_Intl&quot;,GEOGCS[&quot;GCS_North_American_1983&quot;,DATUM[&quot;D_North_American_1983&quot;,SPHEROID[&quot;GRS_1980&quot;,6378137.0,298.257222101]],PRIMEM[&quot;Greenwich&quot;,0.0],UNIT[&quot;Degree&quot;,0.0174532925199433]],PROJECTION[&quot;Lambert_Conformal_Conic&quot;],PARAMETER[&quot;False_Easting&quot;,1312335.958005249],PARAMETER[&quot;False_Northing&quot;,0.0],PARAMETER[&quot;Central_Meridian&quot;,-120.5],PARAMETER[&quot;Standard_Parallel_1&quot;,43.0],PARAMETER[&quot;Standard_Parallel_2&quot;,45.5],PARAMETER[&quot;Latitude_Of_Origin&quot;,41.75],UNIT[&quot;Foot&quot;,0.3048],AUTHORITY[&quot;EPSG&quot;,2992]]</WKT><XOrigin>-118489100</XOrigin><YOrigin>-97381100</YOrigin><XYScale>3048</XYScale><ZOrigin>-100000</ZOrigin><ZScale>10000</ZScale><MOrigin>-100000</MOrigin><MScale>10000</MScale><XYTolerance>0.0032808398950131233</XYTolerance><ZTolerance>0.001</ZTolerance><MTolerance>0.001</MTolerance><HighPrecision>true</HighPrecision><WKID>2992</WKID><LatestWKID>2992</LatestWKID></ProjectedCoordinateSystem> Linear Unit: Foot (0.304800) CalculateField "ofpbds_gdb.GIS.ofpbds_pt Bowers" fpbRmvDt "00000000" VB # CalculateField "ofpbds_gdb.GIS.ofpbds_pt Bowers" fpbRmvDt "00000000" VB # CalculateField "ofpbds_gdb.GIS.ofpbds_pt BowersEdit" fpbRevDt "20190927" VB # CalculateField ofpbds_gdb.GIS.ofpbds_pt fpbRmvDt NULL VB # AddAttachments ofpbds_gdb.GIS.ofpbds_pt fpbFtrID "Z:\Screens & Passage\Screen-Pass\Passage\Fish Psg - Nordholm\Database Management\OfpbDS\2019 List For Pictures.xlsx\Test$" fpbFtrID FilePath # AddAttachments ofpbds_gdb.GIS.ofpbds_pt fpbFtrID "Z:\Screens & Passage\Screen-Pass\Passage\Fish Psg - Nordholm\Database Management\OfpbDS\2019 List For Pictures.xlsx\Upload$" fpbFtrID FilePath # AddAttachments ofpbds_gdb.GIS.ofpbds_pt fpbFtrID "Z:\Screens & Passage\Screen-Pass\Passage\Fish Psg - Nordholm\Database Management\OfpbDS\2019 List For Pictures.xlsx\'2ndtry$'" fpbFtrID FilePath # AddAttachments ofpbds_gdb.GIS.ofpbds_pt fpbFtrID "Z:\Screens & Passage\Screen-Pass\Passage\Fish Psg - Nordholm\Database Management\OfpbDS\2019 List For Pictures.xlsx\Last$" fpbFtrID FilePath # CalculateField ofpbds_gdb.GIS.ofpbds_pt fpbStaEvDt "20200403" VB # CalculateField ofpbds_gdb.GIS.ofpbds_pt fpbFtrID 46683 VB # CalculateField ofpbds_gdb.GIS.ofpbds_pt fpbRevDt "20200508" VB # CalculateField ofpbds_gdb.GIS.ofpbds_pt fpbFPasONm "Elise Kelley" VB # CalculateField ofpbds_gdb.GIS.ofpbds_pt fpbRevDt "20200508" VB # CalculateField ofpbds_gdb.GIS.ofpbds_pt fpbStaEvDt "20200000" VB # CalculateField ofpbds_gdb.GIS.ofpbds_pt fpbFPasONm "Elise Kelley" VB # CalculateField ofpbds_gdb.GIS.ofpbds_pt fpbFPasONm "Elise Kelley" VB # Append JohnDayAndOtherMiscDistrictAdditionsMay2020 ofpbds_gdb.GIS.ofpbds_pt NO_TEST "fpbFtrID "fpbFtrID" true false false 4 Long 0 10 ,First,#,JohnDayAndOtherMiscDistrictAdditionsMay2020,fpbFtrID,-1,-1;fpbLong "fpbLong" true false false 8 Double 8 38 ,First,#;fpbLat "fpbLat" true false false 8 Double 8 38 ,First,#;fpbSiteID "fpbSiteID" true false false 4 Long 0 10 ,First,#;fpbRevDt "fpbRevDt" true true false 8 Text 0 0 ,First,#,JohnDayAndOtherMiscDistrictAdditionsMay2020,fpbRevDt,-1,-1;fpbOFtrID "fpbOFtrID" true false false 40 Text 0 0 ,First,#;fpbONm "fpbONm" true false false 30 Text 0 0 ,First,#,JohnDayAndOtherMiscDistrictAdditionsMay2020,fpbONm,-1,-1;fpbOSiteID "fpbOSiteID" true false false 40 Text 0 0 ,First,#;fpbLocMd "fpbLocMd" true false false 15 Text 0 0 ,First,#,JohnDayAndOtherMiscDistrictAdditionsMay2020,fpbLocMd,-1,-1;fpbLocAccu "fpbLocAccu" true false false 2 Short 0 5 ,First,#,JohnDayAndOtherMiscDistrictAdditionsMay2020,fpbLocAccu,-1,-1;fpbLocDt "fpbLocDt" true true false 8 Text 0 0 ,First,#,JohnDayAndOtherMiscDistrictAdditionsMay2020,fpbLocDt,-1,-1;fpbFtrTy "fpbFtrTy" true false false 25 Text 0 0 ,First,#,JohnDayAndOtherMiscDistrictAdditionsMay2020,fpbFtrTy,-1,-1;fpbFtrNm "fpbFtrNm" true false false 50 Text 0 0 ,First,#,JohnDayAndOtherMiscDistrictAdditionsMay2020,fpbFtrNm,-1,-1;fpbRmvDt "fpbRmvDt" true true false 8 Text 0 0 ,First,#,JohnDayAndOtherMiscDistrictAdditionsMay2020,fpbRmvDt,-1,-1;fpbMltFtr "fpbMltFtr" true false false 7 Text 0 0 ,First,#;fpbFPasSta "fpbFPasSta" true false false 8 Text 0 0 ,First,#,JohnDayAndOtherMiscDistrictAdditionsMay2020,fpbFPasSta,-1,-1;fpbStaEvDt "fpbStaEvDt" true true false 8 Text 0 0 ,First,#,JohnDayAndOtherMiscDistrictAdditionsMay2020,fpbStaEvDt,-1,-1;fpbStaEvMd "fpbStaEvMd" true false false 20 Text 0 0 ,First,#,JohnDayAndOtherMiscDistrictAdditionsMay2020,fpbStaEvMd,-1,-1;fpbFySta "fpbFySta" true false false 20 Text 0 0 ,First,#,JohnDayAndOtherMiscDistrictAdditionsMay2020,fpbFySta,-1,-1;fpbFyCrit "fpbFyCrit" true true false 7 Text 0 0 ,First,#,JohnDayAndOtherMiscDistrictAdditionsMay2020,fpbFyCrit,-1,-1;fpbCrdDesc "fpbCrdDesc" true true false 254 Text 0 0 ,First,#,JohnDayAndOtherMiscDistrictAdditionsMay2020,fpbCrdDesc,-1,-1;Permanent_Identifier "Permanent_Identifier" true false false 40 Text 0 0 ,First,#;ReachCode "ReachCode" true true false 14 Text 0 0 ,First,#;Measure "Measure" true true false 8 Double 3 8 ,First,#;EventDate "EventDate" true true false 8 Date 0 0 ,First,#;ReachSMDate "ReachSMDate" true true false 8 Date 0 0 ,First,#;ReachResolution "ReachResolution" true true false 2 Short 0 5 ,First,#;fpbStrNm "fpbStrNm" true true false 50 Text 0 0 ,First,#,JohnDayAndOtherMiscDistrictAdditionsMay2020,fpbStrNm,-1,-1;fpbRdID "fpbRdID" true true false 13 Text 0 0 ,First,#,JohnDayAndOtherMiscDistrictAdditionsMay2020,fpbRdID,-1,-1;fpbRdMile "fpbRdMile" true true false 8 Double 3 8 ,First,#,JohnDayAndOtherMiscDistrictAdditionsMay2020,fpbRdMile,-1,-1;fpbRdNm "fpbRdNm" true true false 50 Text 0 0 ,First,#,JohnDayAndOtherMiscDistrictAdditionsMay2020,fpbRdNm,-1,-1;fpbLocONm "fpbLocONm" true true false 30 Text 0 0 ,First,#;fpbFtrSTy "fpbFtrSTy" true true false 30 Text 0 0 ,First,#,JohnDayAndOtherMiscDistrictAdditionsMay2020,fpbFtrSTy,-1,-1;fpbFtrNmSr "fpbFtrNmSr" true true false 5 Text 0 0 ,First,#;fpbHeight "fpbHeight" true true false 4 Float 1 4 ,First,#,JohnDayAndOtherMiscDistrictAdditionsMay2020,fpbHeight,-1,-1;fpbLength "fpbLength" true true false 4 Float 1 6 ,First,#,JohnDayAndOtherMiscDistrictAdditionsMay2020,fpbLength,-1,-1;fpbWidth "fpbWidth" true true false 4 Float 1 6 ,First,#,JohnDayAndOtherMiscDistrictAdditionsMay2020,fpbWidth,-1,-1;fpbSlope "fpbSlope" true true false 4 Float 1 4 ,First,#,JohnDayAndOtherMiscDistrictAdditionsMay2020,fpbSlope,-1,-1;fpbDrop "fpbDrop" true true false 4 Float 1 4 ,First,#,JohnDayAndOtherMiscDistrictAdditionsMay2020,fpbDrop,-1,-1;fpbOrYr "fpbOrYr" true true false 4 Text 0 0 ,First,#,JohnDayAndOtherMiscDistrictAdditionsMay2020,fpbOrYr,-1,-1;fpbModDt "fpbModDt" true true false 8 Text 0 0 ,First,#,JohnDayAndOtherMiscDistrictAdditionsMay2020,fpbModDt,-1,-1;fpbModTy "fpbModTy" true true false 10 Text 0 0 ,First,#,JohnDayAndOtherMiscDistrictAdditionsMay2020,fpbModTy,-1,-1;fpbModDesc "fpbModDesc" true true false 254 Text 0 0 ,First,#,JohnDayAndOtherMiscDistrictAdditionsMay2020,fpbModDesc,-1,-1;fpbDesONm "fpbDesONm" true true false 30 Text 0 0 ,First,#;fpbOwn "fpbOwn" true true false 60 Text 0 0 ,First,#,JohnDayAndOtherMiscDistrictAdditionsMay2020,fpbOwn,-1,-1;fpbLOwn "fpbLOwn" true true false 60 Text 0 0 ,First,#,JohnDayAndOtherMiscDistrictAdditionsMay2020,fpbLOwn,-1,-1;fpbOperate "fpbOperate" true true false 60 Text 0 0 ,First,#,JohnDayAndOtherMiscDistrictAdditionsMay2020,fpbOperate,-1,-1;fpbFyOwn "fpbFyOwn" true true false 60 Text 0 0 ,First,#,JohnDayAndOtherMiscDistrictAdditionsMay2020,fpbFyOwn,-1,-1;fpbOwnTy "fpbOwnTy" true true false 15 Text 0 0 ,First,#;fpbLOwnTy "fpbLOwnTy" true true false 15 Text 0 0 ,First,#;fpbOwnONm "fpbOwnONm" true true false 30 Text 0 0 ,First,#;fpbFyTy "fpbFyTy" true true false 15 Text 0 0 ,First,#,JohnDayAndOtherMiscDistrictAdditionsMay2020,fpbFyTy,-1,-1;fpbFySTy "fpbFySTy" true true false 20 Text 0 0 ,First,#,JohnDayAndOtherMiscDistrictAdditionsMay2020,fpbFySTy,-1,-1;fpbFyOrYr "fpbFyOrYr" true true false 4 Text 0 0 ,First,#,JohnDayAndOtherMiscDistrictAdditionsMay2020,fpbFyOrYr,-1,-1;fpbFPasONm "fpbFPasONm" true true false 30 Text 0 0 ,First,#;fpbLocMdD "fpbLocMdD" true true false 100 Text 0 0 ,First,#;fpbFtrTyD "fpbFtrTyD" true true false 100 Text 0 0 ,First,#;fpbFtrSTyD "fpbFtrSTyD" true true false 100 Text 0 0 ,First,#;fpbEvMdFAD "fpbEvMdFAD" true true false 100 Text 0 0 ,First,#;fpbEvMdPAD "fpbEvMdPAD" true true false 100 Text 0 0 ,First,#;fpbFyTyD "fpbFyTyD" true true false 100 Text 0 0 ,First,#;fpbOwnTyD "fpbOwnTyD" true true false 100 Text 0 0 ,First,#;fpbLOwnTyD "fpbLOwnTyD" true true false 100 Text 0 0 ,First,#;fpbComment "fpbComment" true true false 254 Text 0 0 ,First,#,JohnDayAndOtherMiscDistrictAdditionsMay2020,fpbComment,-1,-1;fpbStrID "fpbStrID" true true false 13 Text 0 0 ,First,#;fpbStrMeas "fpbStrMeas" true true false 8 Double 3 8 ,First,#;OWEB_status "OWEB Update" true true false 2 Short 0 0 ,First,#;OWEB_userid "OWEB_userid" true true false 2 Short 0 5 ,First,#;GlobalID "GlobalID" false false false 38 GlobalID 0 0 ,First,#,JohnDayAndOtherMiscDistrictAdditionsMay2020,GlobalID,-1,-1;PriorityGroup "PriorityGroup" true true false 15 Text 0 0 ,First,#" # Append FHD_FPB_Edits.FHDFPBEDITOR.ProposedFPBChanges ofpbds_gdb.GIS.ofpbds_pt NO_TEST "fpbFtrID "fpbFtrID" true false false 4 Long 0 10 ,First,#,FHD_FPB_Edits.FHDFPBEDITOR.ProposedFPBChanges,fpbFtrID,-1,-1;fpbLong "fpbLong" true false false 8 Double 8 38 ,First,#;fpbLat "fpbLat" true false false 8 Double 8 38 ,First,#;fpbSiteID "fpbSiteID" true false false 4 Long 0 10 ,First,#;fpbRevDt "fpbRevDt" true true false 8 Text 0 0 ,First,#,FHD_FPB_Edits.FHDFPBEDITOR.ProposedFPBChanges,fpbRevDt,-1,-1;fpbOFtrID "fpbOFtrID" true false false 40 Text 0 0 ,First,#;fpbONm "fpbONm" true false false 30 Text 0 0 ,First,#,FHD_FPB_Edits.FHDFPBEDITOR.ProposedFPBChanges,fpbONm,-1,-1;fpbOSiteID "fpbOSiteID" true false false 40 Text 0 0 ,First,#;fpbLocMd "fpbLocMd" true false false 15 Text 0 0 ,First,#,FHD_FPB_Edits.FHDFPBEDITOR.ProposedFPBChanges,fpbLocMd,-1,-1;fpbLocAccu "fpbLocAccu" true false false 2 Short 0 5 ,First,#,FHD_FPB_Edits.FHDFPBEDITOR.ProposedFPBChanges,fpbLocAccu,-1,-1;fpbLocDt "fpbLocDt" true true false 8 Text 0 0 ,First,#,FHD_FPB_Edits.FHDFPBEDITOR.ProposedFPBChanges,fpbLocDt,-1,-1;fpbFtrTy "fpbFtrTy" true false false 25 Text 0 0 ,First,#,FHD_FPB_Edits.FHDFPBEDITOR.ProposedFPBChanges,fpbFtrTy,-1,-1;fpbFtrNm "fpbFtrNm" true false false 50 Text 0 0 ,First,#,FHD_FPB_Edits.FHDFPBEDITOR.ProposedFPBChanges,fpbFtrNm,-1,-1;fpbRmvDt "fpbRmvDt" true true false 8 Text 0 0 ,First,#,FHD_FPB_Edits.FHDFPBEDITOR.ProposedFPBChanges,fpbRmvDt,-1,-1;fpbMltFtr "fpbMltFtr" true false false 7 Text 0 0 ,First,#;fpbFPasSta "fpbFPasSta" true false false 8 Text 0 0 ,First,#,FHD_FPB_Edits.FHDFPBEDITOR.ProposedFPBChanges,fpbFPasSta,-1,-1;fpbStaEvDt "fpbStaEvDt" true true false 8 Text 0 0 ,First,#,FHD_FPB_Edits.FHDFPBEDITOR.ProposedFPBChanges,fpbStaEvDt,-1,-1;fpbStaEvMd "fpbStaEvMd" true false false 20 Text 0 0 ,First,#,FHD_FPB_Edits.FHDFPBEDITOR.ProposedFPBChanges,fpbStaEvMd,-1,-1;fpbFySta "fpbFySta" true false false 20 Text 0 0 ,First,#,FHD_FPB_Edits.FHDFPBEDITOR.ProposedFPBChanges,fpbFySta,-1,-1;fpbFyCrit "fpbFyCrit" true true false 7 Text 0 0 ,First,#,FHD_FPB_Edits.FHDFPBEDITOR.ProposedFPBChanges,fpbFyCrit,-1,-1;fpbCrdDesc "fpbCrdDesc" true true false 254 Text 0 0 ,First,#,FHD_FPB_Edits.FHDFPBEDITOR.ProposedFPBChanges,fpbCrdDesc,-1,-1;Permanent_Identifier "Permanent_Identifier" true false false 40 Text 0 0 ,First,#;ReachCode "ReachCode" true true false 14 Text 0 0 ,First,#;Measure "Measure" true true false 8 Double 3 8 ,First,#;EventDate "EventDate" true true false 8 Date 0 0 ,First,#;ReachSMDate "ReachSMDate" true true false 8 Date 0 0 ,First,#;ReachResolution "ReachResolution" true true false 2 Short 0 5 ,First,#;fpbStrNm "fpbStrNm" true true false 50 Text 0 0 ,First,#,FHD_FPB_Edits.FHDFPBEDITOR.ProposedFPBChanges,fpbStrNm,-1,-1;fpbRdID "fpbRdID" true true false 13 Text 0 0 ,First,#,FHD_FPB_Edits.FHDFPBEDITOR.ProposedFPBChanges,fpbRdID,-1,-1;fpbRdMile "fpbRdMile" true true false 8 Double 3 8 ,First,#,FHD_FPB_Edits.FHDFPBEDITOR.ProposedFPBChanges,fpbRdMile,-1,-1;fpbRdNm "fpbRdNm" true true false 50 Text 0 0 ,First,#,FHD_FPB_Edits.FHDFPBEDITOR.ProposedFPBChanges,fpbRdNm,-1,-1;fpbLocONm "fpbLocONm" true true false 30 Text 0 0 ,First,#;fpbFtrSTy "fpbFtrSTy" true true false 30 Text 0 0 ,First,#,FHD_FPB_Edits.FHDFPBEDITOR.ProposedFPBChanges,fpbFtrSTy,-1,-1;fpbFtrNmSr "fpbFtrNmSr" true true false 5 Text 0 0 ,First,#;fpbHeight "fpbHeight" true true false 4 Float 1 4 ,First,#,FHD_FPB_Edits.FHDFPBEDITOR.ProposedFPBChanges,fpbHeight,-1,-1;fpbLength "fpbLength" true true false 4 Float 1 6 ,First,#,FHD_FPB_Edits.FHDFPBEDITOR.ProposedFPBChanges,fpbLength,-1,-1;fpbWidth "fpbWidth" true true false 4 Float 1 6 ,First,#,FHD_FPB_Edits.FHDFPBEDITOR.ProposedFPBChanges,fpbWidth,-1,-1;fpbSlope "fpbSlope" true true false 4 Float 1 4 ,First,#,FHD_FPB_Edits.FHDFPBEDITOR.ProposedFPBChanges,fpbSlope,-1,-1;fpbDrop "fpbDrop" true true false 4 Float 1 4 ,First,#,FHD_FPB_Edits.FHDFPBEDITOR.ProposedFPBChanges,fpbDrop,-1,-1;fpbOrYr "fpbOrYr" true true false 4 Text 0 0 ,First,#,FHD_FPB_Edits.FHDFPBEDITOR.ProposedFPBChanges,fpbOrYr,-1,-1;fpbModDt "fpbModDt" true true false 8 Text 0 0 ,First,#,FHD_FPB_Edits.FHDFPBEDITOR.ProposedFPBChanges,fpbModDt,-1,-1;fpbModTy "fpbModTy" true true false 10 Text 0 0 ,First,#,FHD_FPB_Edits.FHDFPBEDITOR.ProposedFPBChanges,fpbModTy,-1,-1;fpbModDesc "fpbModDesc" true true false 254 Text 0 0 ,First,#,FHD_FPB_Edits.FHDFPBEDITOR.ProposedFPBChanges,fpbModDesc,-1,-1;fpbDesONm "fpbDesONm" true true false 30 Text 0 0 ,First,#;fpbOwn "fpbOwn" true true false 60 Text 0 0 ,First,#,FHD_FPB_Edits.FHDFPBEDITOR.ProposedFPBChanges,fpbOwn,-1,-1;fpbLOwn "fpbLOwn" true true false 60 Text 0 0 ,First,#,FHD_FPB_Edits.FHDFPBEDITOR.ProposedFPBChanges,fpbLOwn,-1,-1;fpbOperate "fpbOperate" true true false 60 Text 0 0 ,First,#,FHD_FPB_Edits.FHDFPBEDITOR.ProposedFPBChanges,fpbOperate,-1,-1;fpbFyOwn "fpbFyOwn" true true false 60 Text 0 0 ,First,#,FHD_FPB_Edits.FHDFPBEDITOR.ProposedFPBChanges,fpbFyOwn,-1,-1;fpbOwnTy "fpbOwnTy" true true false 15 Text 0 0 ,First,#;fpbLOwnTy "fpbLOwnTy" true true false 15 Text 0 0 ,First,#;fpbOwnONm "fpbOwnONm" true true false 30 Text 0 0 ,First,#;fpbFyTy "fpbFyTy" true true false 15 Text 0 0 ,First,#,FHD_FPB_Edits.FHDFPBEDITOR.ProposedFPBChanges,fpbFyTy,-1,-1;fpbFySTy "fpbFySTy" true true false 20 Text 0 0 ,First,#,FHD_FPB_Edits.FHDFPBEDITOR.ProposedFPBChanges,fpbFySTy,-1,-1;fpbFyOrYr "fpbFyOrYr" true true false 4 Text 0 0 ,First,#,FHD_FPB_Edits.FHDFPBEDITOR.ProposedFPBChanges,fpbFyOrYr,-1,-1;fpbFPasONm "fpbFPasONm" true true false 30 Text 0 0 ,First,#;fpbLocMdD "fpbLocMdD" true true false 100 Text 0 0 ,First,#;fpbFtrTyD "fpbFtrTyD" true true false 100 Text 0 0 ,First,#;fpbFtrSTyD "fpbFtrSTyD" true true false 100 Text 0 0 ,First,#;fpbEvMdFAD "fpbEvMdFAD" true true false 100 Text 0 0 ,First,#;fpbEvMdPAD "fpbEvMdPAD" true true false 100 Text 0 0 ,First,#;fpbFyTyD "fpbFyTyD" true true false 100 Text 0 0 ,First,#;fpbOwnTyD "fpbOwnTyD" true true false 100 Text 0 0 ,First,#;fpbLOwnTyD "fpbLOwnTyD" true true false 100 Text 0 0 ,First,#;fpbComment "fpbComment" true true false 254 Text 0 0 ,First,#,FHD_FPB_Edits.FHDFPBEDITOR.ProposedFPBChanges,fpbComment,-1,-1;fpbStrID "fpbStrID" true true false 13 Text 0 0 ,First,#;fpbStrMeas "fpbStrMeas" true true false 8 Double 3 8 ,First,#;OWEB_status "OWEB Update" true true false 2 Short 0 0 ,First,#;OWEB_userid "OWEB_userid" true true false 2 Short 0 5 ,First,#;GlobalID "GlobalID" false false false 38 GlobalID 0 0 ,First,#,FHD_FPB_Edits.FHDFPBEDITOR.ProposedFPBChanges,GlobalID,-1,-1;PriorityGroup "PriorityGroup" true true false 15 Text 0 0 ,First,#" # CalculateField ofpbds_gdb.GIS.ofpbds_pt fpbFtrID "[OBJECTID] - 34858" VB # CalculateField ofpbds_gdb.GIS.ofpbds_pt fpbSiteID [fpbFtrID] VB # CalculateField ofpbds_gdb.GIS.ofpbds_pt fpbOFtrID [fpbFtrID] VB # CalculateField ofpbds_gdb.GIS.ofpbds_pt fpbOSiteID [fpbFtrID] VB # CalculateField ofpbds_gdb.GIS.ofpbds_pt fpbLocMd "FieldGPS" VB # AddAttachments ofpbds_gdb.GIS.ofpbds_pt fpbFtrID AttachmentsTable fpbFtrID Path2 # CalculateField ofpbds_gdb.GIS.ofpbds_pt fpbFtrID "[OBJECTID] - 33838" VB # CalculateField ofpbds_gdb.GIS.ofpbds_pt fpbSiteID [fpbFtrID] VB # CalculateField ofpbds_gdb.GIS.ofpbds_pt fpbOFtrID [fpbFtrID] VB # CalculateField ofpbds_gdb.GIS.ofpbds_pt fpbOSiteID [fpbFtrID] VB # Append DFMSdata ofpbds_gdb.GIS.ofpbds_pt NO_TEST "fpbFtrID "fpbFtrID" true false false 4 Long 0 10 ,First,#,DFMSdata,fpbFtrID,-1,-1;fpbLong "fpbLong" true false false 8 Double 8 38 ,First,#,DFMSdata,fpbLong,-1,-1;fpbLat "fpbLat" true false false 8 Double 8 38 ,First,#,DFMSdata,fpbLat,-1,-1;fpbSiteID "fpbSiteID" true false false 4 Long 0 10 ,First,#,DFMSdata,fpbSiteID,-1,-1;fpbRevDt "fpbRevDt" true true false 8 Text 0 0 ,First,#,DFMSdata,fpbRevDt,-1,-1;fpbOFtrID "fpbOFtrID" true false false 40 Text 0 0 ,First,#,DFMSdata,fpbOFtrID,-1,-1;fpbONm "fpbONm" true false false 30 Text 0 0 ,First,#,DFMSdata,fpbONm,-1,-1;fpbOSiteID "fpbOSiteID" true false false 40 Text 0 0 ,First,#,DFMSdata,fpbOSiteID,-1,-1;fpbLocMd "fpbLocMd" true false false 15 Text 0 0 ,First,#,DFMSdata,fpbLocMd,-1,-1;fpbLocAccu "fpbLocAccu" true false false 2 Short 0 5 ,First,#,DFMSdata,fpbLocAccu,-1,-1;fpbLocDt "fpbLocDt" true true false 8 Text 0 0 ,First,#,DFMSdata,fpbLocDt,-1,-1;fpbFtrTy "fpbFtrTy" true false false 25 Text 0 0 ,First,#,DFMSdata,fpbFtrTy,-1,-1;fpbFtrNm "fpbFtrNm" true false false 50 Text 0 0 ,First,#,DFMSdata,fpbFtrNm,-1,-1;fpbRmvDt "fpbRmvDt" true true false 8 Text 0 0 ,First,#,DFMSdata,fpbRmvDt,-1,-1;fpbMltFtr "fpbMltFtr" true false false 7 Text 0 0 ,First,#,DFMSdata,fpbMltFtr,-1,-1;fpbFPasSta "fpbFPasSta" true false false 8 Text 0 0 ,First,#,DFMSdata,fpbFPasSta,-1,-1;fpbStaEvDt "fpbStaEvDt" true true false 8 Text 0 0 ,First,#,DFMSdata,fpbStaEvDt,-1,-1;fpbStaEvMd "fpbStaEvMd" true false false 20 Text 0 0 ,First,#,DFMSdata,fpbStaEvMd,-1,-1;fpbFySta "fpbFySta" true false false 20 Text 0 0 ,First,#,DFMSdata,fpbFySta,-1,-1;fpbFyCrit "fpbFyCrit" true true false 7 Text 0 0 ,First,#,DFMSdata,fpbFyCrit,-1,-1;fpbCrdDesc "fpbCrdDesc" true true false 254 Text 0 0 ,First,#,DFMSdata,fpbCrdDesc,-1,-1;Permanent_Identifier "Permanent_Identifier" true false false 40 Text 0 0 ,First,#;ReachCode "ReachCode" true true false 14 Text 0 0 ,First,#;Measure "Measure" true true false 8 Double 3 8 ,First,#;EventDate "EventDate" true true false 8 Date 0 0 ,First,#;ReachSMDate "ReachSMDate" true true false 8 Date 0 0 ,First,#;ReachResolution "ReachResolution" true true false 2 Short 0 5 ,First,#;fpbStrNm "fpbStrNm" true true false 50 Text 0 0 ,First,#,DFMSdata,fpbStrNm,-1,-1;fpbRdID "fpbRdID" true true false 13 Text 0 0 ,First,#,DFMSdata,fpbRdID,-1,-1;fpbRdMile "fpbRdMile" true true false 8 Double 3 8 ,First,#,DFMSdata,fpbRdMile,-1,-1;fpbRdNm "fpbRdNm" true true false 50 Text 0 0 ,First,#,DFMSdata,fpbRdNm,-1,-1;fpbLocONm "fpbLocONm" true true false 30 Text 0 0 ,First,#,DFMSdata,fpbLocONm,-1,-1;fpbFtrSTy "fpbFtrSTy" true true false 30 Text 0 0 ,First,#,DFMSdata,fpbFtrSTy,-1,-1;fpbFtrNmSr "fpbFtrNmSr" true true false 5 Text 0 0 ,First,#,DFMSdata,fpbFtrNmSr,-1,-1;fpbHeight "fpbHeight" true true false 4 Float 1 4 ,First,#,DFMSdata,fpbHeight,-1,-1;fpbLength "fpbLength" true true false 4 Float 1 6 ,First,#,DFMSdata,fpbLength,-1,-1;fpbWidth "fpbWidth" true true false 4 Float 1 6 ,First,#,DFMSdata,fpbWidth,-1,-1;fpbSlope "fpbSlope" true true false 4 Float 1 4 ,First,#,DFMSdata,fpbSlope,-1,-1;fpbDrop "fpbDrop" true true false 4 Float 1 4 ,First,#,DFMSdata,fpbDrop,-1,-1;fpbOrYr "fpbOrYr" true true false 4 Text 0 0 ,First,#,DFMSdata,fpbOrYr,-1,-1;fpbModDt "fpbModDt" true true false 8 Text 0 0 ,First,#,DFMSdata,fpbModDt,-1,-1;fpbModTy "fpbModTy" true true false 10 Text 0 0 ,First,#,DFMSdata,fpbModTy,-1,-1;fpbModDesc "fpbModDesc" true true false 254 Text 0 0 ,First,#,DFMSdata,fpbModDesc,-1,-1;fpbDesONm "fpbDesONm" true true false 30 Text 0 0 ,First,#,DFMSdata,fpbDesONm,-1,-1;fpbOwn "fpbOwn" true true false 60 Text 0 0 ,First,#,DFMSdata,fpbOwn,-1,-1;fpbLOwn "fpbLOwn" true true false 60 Text 0 0 ,First,#,DFMSdata,fpbLOwn,-1,-1;fpbOperate "fpbOperate" true true false 60 Text 0 0 ,First,#,DFMSdata,fpbOperate,-1,-1;fpbFyOwn "fpbFyOwn" true true false 60 Text 0 0 ,First,#,DFMSdata,fpbFyOwn,-1,-1;fpbOwnTy "fpbOwnTy" true true false 15 Text 0 0 ,First,#,DFMSdata,fpbOwnTy,-1,-1;fpbLOwnTy "fpbLOwnTy" true true false 15 Text 0 0 ,First,#,DFMSdata,fpbLOwnTy,-1,-1;fpbOwnONm "fpbOwnONm" true true false 30 Text 0 0 ,First,#,DFMSdata,fpbOwnONm,-1,-1;fpbFyTy "fpbFyTy" true true false 15 Text 0 0 ,First,#,DFMSdata,fpbFyTy,-1,-1;fpbFySTy "fpbFySTy" true true false 20 Text 0 0 ,First,#,DFMSdata,fpbFySTy,-1,-1;fpbFyOrYr "fpbFyOrYr" true true false 4 Text 0 0 ,First,#,DFMSdata,fpbFyOrYr,-1,-1;fpbFPasONm "fpbFPasONm" true true false 30 Text 0 0 ,First,#,DFMSdata,fpbFPasONm,-1,-1;fpbLocMdD "fpbLocMdD" true true false 100 Text 0 0 ,First,#,DFMSdata,fpbLocMdD,-1,-1;fpbFtrTyD "fpbFtrTyD" true true false 100 Text 0 0 ,First,#,DFMSdata,fpbFtrTyD,-1,-1;fpbFtrSTyD "fpbFtrSTyD" true true false 100 Text 0 0 ,First,#,DFMSdata,fpbFtrSTyD,-1,-1;fpbEvMdFAD "fpbEvMdFAD" true true false 100 Text 0 0 ,First,#,DFMSdata,fpbEvMdFAD,-1,-1;fpbEvMdPAD "fpbEvMdPAD" true true false 100 Text 0 0 ,First,#,DFMSdata,fpbEvMdPAD,-1,-1;fpbFyTyD "fpbFyTyD" true true false 100 Text 0 0 ,First,#,DFMSdata,fpbFyTyD,-1,-1;fpbOwnTyD "fpbOwnTyD" true true false 100 Text 0 0 ,First,#,DFMSdata,fpbOwnTyD,-1,-1;fpbLOwnTyD "fpbLOwnTyD" true true false 100 Text 0 0 ,First,#,DFMSdata,fpbLOwnTyD,-1,-1;fpbComment "fpbComment" true true false 254 Text 0 0 ,First,#,DFMSdata,fpbComment,-1,-1;fpbStrID "fpbStrID" true true false 13 Text 0 0 ,First,#;fpbStrMeas "fpbStrMeas" true true false 8 Double 3 8 ,First,#;OWEB_status "OWEB Update" true true false 2 Short 0 0 ,First,#;OWEB_userid "OWEB_userid" true true false 2 Short 0 5 ,First,#;GlobalID "GlobalID" false false false 38 GlobalID 0 0 ,First,#;PriorityGroup "PriorityGroup" true true false 15 Text 0 0 ,First,#" # CalculateField ofpbds_gdb.GIS.ofpbds_pt fpbRmvDt NULL VB # CalculateField ofpbds_gdb.GIS.ofpbds_pt fpbRevDt "20210407" VB # CalculateField "ofpbds_gdb.GIS.ofpbds_pt - Kregg" fpbSiteID [fpbFtrID] VB # CalculateField "ofpbds_gdb.GIS.ofpbds_pt - Kregg" fpbOFtrID [fpbFtrID] VB # CalculateField "ofpbds_gdb.GIS.ofpbds_pt - Kregg" fpbOSiteID [fpbFtrID] VB # Append UnmatchedMultiplePipes_All2 ofpbds_gdb.GIS.ofpbds_pt "Use the field map to reconcile field differences" "fpbFtrID "fpbFtrID" true false false 4 Long 0 10,First,#,\\fwhqd\home\nordhoka\My Documents\ArcGIS\Projects\fpbDS Database Updates\Database Updates.gdb\UnmatchedMultiplePipes_All2,fpbFtrID,-1,-1;fpbLong "fpbLong" true false false 8 Double 8 38,First,#,\\fwhqd\home\nordhoka\My Documents\ArcGIS\Projects\fpbDS Database Updates\Database Updates.gdb\UnmatchedMultiplePipes_All2,fpbLong,-1,-1;fpbLat "fpbLat" true false false 8 Double 8 38,First,#,\\fwhqd\home\nordhoka\My Documents\ArcGIS\Projects\fpbDS Database Updates\Database Updates.gdb\UnmatchedMultiplePipes_All2,fpbLat,-1,-1;fpbSiteID "fpbSiteID" true false false 4 Long 0 10,First,#,\\fwhqd\home\nordhoka\My Documents\ArcGIS\Projects\fpbDS Database Updates\Database Updates.gdb\UnmatchedMultiplePipes_All2,fpbSiteID,-1,-1;fpbRevDt "fpbRevDt" true true false 8 Text 0 0,First,#,\\fwhqd\home\nordhoka\My Documents\ArcGIS\Projects\fpbDS Database Updates\Database Updates.gdb\UnmatchedMultiplePipes_All2,fpbRevDt,0,8;fpbOFtrID "fpbOFtrID" true false false 40 Text 0 0,First,#,\\fwhqd\home\nordhoka\My Documents\ArcGIS\Projects\fpbDS Database Updates\Database Updates.gdb\UnmatchedMultiplePipes_All2,fpbOFtrID,0,40;fpbONm "fpbONm" true false false 30 Text 0 0,First,#,\\fwhqd\home\nordhoka\My Documents\ArcGIS\Projects\fpbDS Database Updates\Database Updates.gdb\UnmatchedMultiplePipes_All2,fpbONm,0,30;fpbOSiteID "fpbOSiteID" true false false 40 Text 0 0,First,#,\\fwhqd\home\nordhoka\My Documents\ArcGIS\Projects\fpbDS Database Updates\Database Updates.gdb\UnmatchedMultiplePipes_All2,fpbOSiteID,0,40;fpbLocMd "fpbLocMd" true false false 15 Text 0 0,First,#,\\fwhqd\home\nordhoka\My Documents\ArcGIS\Projects\fpbDS Database Updates\Database Updates.gdb\UnmatchedMultiplePipes_All2,fpbLocMd,0,15;fpbLocAccu "fpbLocAccu" true false false 2 Short 0 5,First,#,\\fwhqd\home\nordhoka\My Documents\ArcGIS\Projects\fpbDS Database Updates\Database Updates.gdb\UnmatchedMultiplePipes_All2,fpbLocAccu,-1,-1;fpbLocDt "fpbLocDt" true true false 8 Text 0 0,First,#,\\fwhqd\home\nordhoka\My Documents\ArcGIS\Projects\fpbDS Database Updates\Database Updates.gdb\UnmatchedMultiplePipes_All2,fpbLocDt,0,8;fpbFtrTy "fpbFtrTy" true false false 25 Text 0 0,First,#,\\fwhqd\home\nordhoka\My Documents\ArcGIS\Projects\fpbDS Database Updates\Database Updates.gdb\UnmatchedMultiplePipes_All2,fpbFtrTy,0,25;fpbFtrNm "fpbFtrNm" true false false 50 Text 0 0,First,#,\\fwhqd\home\nordhoka\My Documents\ArcGIS\Projects\fpbDS Database Updates\Database Updates.gdb\UnmatchedMultiplePipes_All2,fpbFtrNm,0,50;fpbRmvDt "fpbRmvDt" true true false 8 Text 0 0,First,#,\\fwhqd\home\nordhoka\My Documents\ArcGIS\Projects\fpbDS Database Updates\Database Updates.gdb\UnmatchedMultiplePipes_All2,fpbRmvDt,0,8;fpbMltFtr "fpbMltFtr" true false false 7 Text 0 0,First,#,\\fwhqd\home\nordhoka\My Documents\ArcGIS\Projects\fpbDS Database Updates\Database Updates.gdb\UnmatchedMultiplePipes_All2,fpbMltFtr,0,7;fpbFPasSta "fpbFPasSta" true false false 8 Text 0 0,First,#,\\fwhqd\home\nordhoka\My Documents\ArcGIS\Projects\fpbDS Database Updates\Database Updates.gdb\UnmatchedMultiplePipes_All2,fpbFPasSta,0,8;fpbStaEvDt "fpbStaEvDt" true true false 8 Text 0 0,First,#,\\fwhqd\home\nordhoka\My Documents\ArcGIS\Projects\fpbDS Database Updates\Database Updates.gdb\UnmatchedMultiplePipes_All2,fpbStaEvDt,0,8;fpbStaEvMd "fpbStaEvMd" true false false 20 Text 0 0,First,#,\\fwhqd\home\nordhoka\My Documents\ArcGIS\Projects\fpbDS Database Updates\Database Updates.gdb\UnmatchedMultiplePipes_All2,fpbStaEvMd,0,20;fpbFySta "fpbFySta" true false false 20 Text 0 0,First,#,\\fwhqd\home\nordhoka\My Documents\ArcGIS\Projects\fpbDS Database Updates\Database Updates.gdb\UnmatchedMultiplePipes_All2,fpbFySta,0,20;fpbFyCrit "fpbFyCrit" true true false 7 Text 0 0,First,#,\\fwhqd\home\nordhoka\My Documents\ArcGIS\Projects\fpbDS Database Updates\Database Updates.gdb\UnmatchedMultiplePipes_All2,fpbFyCrit,0,7;fpbCrdDesc "fpbCrdDesc" true true false 254 Text 0 0,First,#,\\fwhqd\home\nordhoka\My Documents\ArcGIS\Projects\fpbDS Database Updates\Database Updates.gdb\UnmatchedMultiplePipes_All2,fpbCrdDesc,0,254;Permanent_Identifier "Permanent_Identifier" true false false 40 Text 0 0,First,#;ReachCode "ReachCode" true true false 14 Text 0 0,First,#;Measure "Measure" true true false 8 Double 3 8,First,#;EventDate "EventDate" true true false 8 Date 0 0,First,#;ReachSMDate "ReachSMDate" true true false 8 Date 0 0,First,#;ReachResolution "ReachResolution" true true false 2 Short 0 5,First,#;fpbStrNm "fpbStrNm" true true false 50 Text 0 0,First,#,\\fwhqd\home\nordhoka\My Documents\ArcGIS\Projects\fpbDS Database Updates\Database Updates.gdb\UnmatchedMultiplePipes_All2,fpbStrNm,0,50;fpbRdID "fpbRdID" true true false 13 Text 0 0,First,#,\\fwhqd\home\nordhoka\My Documents\ArcGIS\Projects\fpbDS Database Updates\Database Updates.gdb\UnmatchedMultiplePipes_All2,fpbRdID,0,13;fpbRdMile "fpbRdMile" true true false 8 Double 3 8,First,#,\\fwhqd\home\nordhoka\My Documents\ArcGIS\Projects\fpbDS Database Updates\Database Updates.gdb\UnmatchedMultiplePipes_All2,fpbRdMile,-1,-1;fpbRdNm "fpbRdNm" true true false 50 Text 0 0,First,#,\\fwhqd\home\nordhoka\My Documents\ArcGIS\Projects\fpbDS Database Updates\Database Updates.gdb\UnmatchedMultiplePipes_All2,fpbRdNm,0,50;fpbLocONm "fpbLocONm" true true false 30 Text 0 0,First,#,\\fwhqd\home\nordhoka\My Documents\ArcGIS\Projects\fpbDS Database Updates\Database Updates.gdb\UnmatchedMultiplePipes_All2,fpbLocONm,0,30;fpbFtrSTy "fpbFtrSTy" true true false 30 Text 0 0,First,#,\\fwhqd\home\nordhoka\My Documents\ArcGIS\Projects\fpbDS Database Updates\Database Updates.gdb\UnmatchedMultiplePipes_All2,fpbFtrSTy,0,30;fpbFtrNmSr "fpbFtrNmSr" true true false 5 Text 0 0,First,#,\\fwhqd\home\nordhoka\My Documents\ArcGIS\Projects\fpbDS Database Updates\Database Updates.gdb\UnmatchedMultiplePipes_All2,fpbFtrNmSr,0,5;fpbHeight "fpbHeight" true true false 4 Float 1 4,First,#,\\fwhqd\home\nordhoka\My Documents\ArcGIS\Projects\fpbDS Database Updates\Database Updates.gdb\UnmatchedMultiplePipes_All2,fpbHeight,-1,-1;fpbLength "fpbLength" true true false 4 Float 1 6,First,#,\\fwhqd\home\nordhoka\My Documents\ArcGIS\Projects\fpbDS Database Updates\Database Updates.gdb\UnmatchedMultiplePipes_All2,fpbLength,-1,-1;fpbWidth "fpbWidth" true true false 4 Float 1 6,First,#,\\fwhqd\home\nordhoka\My Documents\ArcGIS\Projects\fpbDS Database Updates\Database Updates.gdb\UnmatchedMultiplePipes_All2,fpbWidth,-1,-1;fpbSlope "fpbSlope" true true false 4 Float 1 4,First,#,\\fwhqd\home\nordhoka\My Documents\ArcGIS\Projects\fpbDS Database Updates\Database Updates.gdb\UnmatchedMultiplePipes_All2,fpbSlope,-1,-1;fpbDrop "fpbDrop" true true false 4 Float 1 4,First,#,\\fwhqd\home\nordhoka\My Documents\ArcGIS\Projects\fpbDS Database Updates\Database Updates.gdb\UnmatchedMultiplePipes_All2,fpbDrop,-1,-1;fpbOrYr "fpbOrYr" true true false 4 Text 0 0,First,#,\\fwhqd\home\nordhoka\My Documents\ArcGIS\Projects\fpbDS Database Updates\Database Updates.gdb\UnmatchedMultiplePipes_All2,fpbOrYr,0,4;fpbModDt "fpbModDt" true true false 8 Text 0 0,First,#,\\fwhqd\home\nordhoka\My Documents\ArcGIS\Projects\fpbDS Database Updates\Database Updates.gdb\UnmatchedMultiplePipes_All2,fpbModDt,0,8;fpbModTy "fpbModTy" true true false 10 Text 0 0,First,#,\\fwhqd\home\nordhoka\My Documents\ArcGIS\Projects\fpbDS Database Updates\Database Updates.gdb\UnmatchedMultiplePipes_All2,fpbModTy,0,10;fpbModDesc "fpbModDesc" true true false 254 Text 0 0,First,#,\\fwhqd\home\nordhoka\My Documents\ArcGIS\Projects\fpbDS Database Updates\Database Updates.gdb\UnmatchedMultiplePipes_All2,fpbModDesc,0,254;fpbDesONm "fpbDesONm" true true false 30 Text 0 0,First,#,\\fwhqd\home\nordhoka\My Documents\ArcGIS\Projects\fpbDS Database Updates\Database Updates.gdb\UnmatchedMultiplePipes_All2,fpbDesONm,0,30;fpbOwn "fpbOwn" true true false 60 Text 0 0,First,#,\\fwhqd\home\nordhoka\My Documents\ArcGIS\Projects\fpbDS Database Updates\Database Updates.gdb\UnmatchedMultiplePipes_All2,fpbOwn,0,60;fpbLOwn "fpbLOwn" true true false 60 Text 0 0,First,#,\\fwhqd\home\nordhoka\My Documents\ArcGIS\Projects\fpbDS Database Updates\Database Updates.gdb\UnmatchedMultiplePipes_All2,fpbLOwn,0,60;fpbOperate "fpbOperate" true true false 60 Text 0 0,First,#,\\fwhqd\home\nordhoka\My Documents\ArcGIS\Projects\fpbDS Database Updates\Database Updates.gdb\UnmatchedMultiplePipes_All2,fpbOperate,0,60;fpbFyOwn "fpbFyOwn" true true false 60 Text 0 0,First,#,\\fwhqd\home\nordhoka\My Documents\ArcGIS\Projects\fpbDS Database Updates\Database Updates.gdb\UnmatchedMultiplePipes_All2,fpbFyOwn,0,60;fpbOwnTy "fpbOwnTy" true true false 15 Text 0 0,First,#,\\fwhqd\home\nordhoka\My Documents\ArcGIS\Projects\fpbDS Database Updates\Database Updates.gdb\UnmatchedMultiplePipes_All2,fpbOwnTy,0,15;fpbLOwnTy "fpbLOwnTy" true true false 15 Text 0 0,First,#,\\fwhqd\home\nordhoka\My Documents\ArcGIS\Projects\fpbDS Database Updates\Database Updates.gdb\UnmatchedMultiplePipes_All2,fpbLOwnTy,0,15;fpbOwnONm "fpbOwnONm" true true false 30 Text 0 0,First,#,\\fwhqd\home\nordhoka\My Documents\ArcGIS\Projects\fpbDS Database Updates\Database Updates.gdb\UnmatchedMultiplePipes_All2,fpbOwnONm,0,30;fpbFyTy "fpbFyTy" true true false 15 Text 0 0,First,#,\\fwhqd\home\nordhoka\My Documents\ArcGIS\Projects\fpbDS Database Updates\Database Updates.gdb\UnmatchedMultiplePipes_All2,fpbFyTy,0,15;fpbFySTy "fpbFySTy" true true false 20 Text 0 0,First,#,\\fwhqd\home\nordhoka\My Documents\ArcGIS\Projects\fpbDS Database Updates\Database Updates.gdb\UnmatchedMultiplePipes_All2,fpbFySTy,0,20;fpbFyOrYr "fpbFyOrYr" true true false 4 Text 0 0,First,#,\\fwhqd\home\nordhoka\My Documents\ArcGIS\Projects\fpbDS Database Updates\Database Updates.gdb\UnmatchedMultiplePipes_All2,fpbFyOrYr,0,4;fpbFPasONm "fpbFPasONm" true true false 30 Text 0 0,First,#,\\fwhqd\home\nordhoka\My Documents\ArcGIS\Projects\fpbDS Database Updates\Database Updates.gdb\UnmatchedMultiplePipes_All2,fpbFPasONm,0,30;fpbLocMdD "fpbLocMdD" true true false 100 Text 0 0,First,#,\\fwhqd\home\nordhoka\My Documents\ArcGIS\Projects\fpbDS Database Updates\Database Updates.gdb\UnmatchedMultiplePipes_All2,fpbLocMdD,0,100;fpbFtrTyD "fpbFtrTyD" true true false 100 Text 0 0,First,#,\\fwhqd\home\nordhoka\My Documents\ArcGIS\Projects\fpbDS Database Updates\Database Updates.gdb\UnmatchedMultiplePipes_All2,fpbFtrTyD,0,100;fpbFtrSTyD "fpbFtrSTyD" true true false 100 Text 0 0,First,#,\\fwhqd\home\nordhoka\My Documents\ArcGIS\Projects\fpbDS Database Updates\Database Updates.gdb\UnmatchedMultiplePipes_All2,fpbFtrSTyD,0,100;fpbEvMdFAD "fpbEvMdFAD" true true false 100 Text 0 0,First,#,\\fwhqd\home\nordhoka\My Documents\ArcGIS\Projects\fpbDS Database Updates\Database Updates.gdb\UnmatchedMultiplePipes_All2,fpbEvMdFAD,0,100;fpbEvMdPAD "fpbEvMdPAD" true true false 100 Text 0 0,First,#,\\fwhqd\home\nordhoka\My Documents\ArcGIS\Projects\fpbDS Database Updates\Database Updates.gdb\UnmatchedMultiplePipes_All2,fpbEvMdPAD,0,100;fpbFyTyD "fpbFyTyD" true true false 100 Text 0 0,First,#,\\fwhqd\home\nordhoka\My Documents\ArcGIS\Projects\fpbDS Database Updates\Database Updates.gdb\UnmatchedMultiplePipes_All2,fpbFyTyD,0,100;fpbOwnTyD "fpbOwnTyD" true true false 100 Text 0 0,First,#,\\fwhqd\home\nordhoka\My Documents\ArcGIS\Projects\fpbDS Database Updates\Database Updates.gdb\UnmatchedMultiplePipes_All2,fpbOwnTyD,0,100;fpbLOwnTyD "fpbLOwnTyD" true true false 100 Text 0 0,First,#,\\fwhqd\home\nordhoka\My Documents\ArcGIS\Projects\fpbDS Database Updates\Database Updates.gdb\UnmatchedMultiplePipes_All2,fpbLOwnTyD,0,100;fpbComment "fpbComment" true true false 254 Text 0 0,First,#,\\fwhqd\home\nordhoka\My Documents\ArcGIS\Projects\fpbDS Database Updates\Database Updates.gdb\UnmatchedMultiplePipes_All2,fpbComment,0,254;fpbStrID "fpbStrID" true true false 13 Text 0 0,First,#,\\fwhqd\home\nordhoka\My Documents\ArcGIS\Projects\fpbDS Database Updates\Database Updates.gdb\UnmatchedMultiplePipes_All2,fpbStrID,0,13;fpbStrMeas "fpbStrMeas" true true false 8 Double 3 8,First,#,\\fwhqd\home\nordhoka\My Documents\ArcGIS\Projects\fpbDS Database Updates\Database Updates.gdb\UnmatchedMultiplePipes_All2,fpbStrMeas,-1,-1;OWEB_status "OWEB Update" true true false 2 Short 0 0,First,#;OWEB_userid "OWEB_userid" true true false 2 Short 0 5,First,#;GlobalID "GlobalID" false false true 38 GlobalID 0 0,First,#;PriorityGroup "PriorityGroup" true true false 15 Text 0 0,First,#" # # Append Features_New ofpbds_gdb.GIS.ofpbds_pt "Use the field map to reconcile field differences" "fpbFtrID "fpbFtrID" true false false 4 Long 0 10,First,#,\\fwhqd\home\nordhoka\My Documents\ArcGIS\Projects\fpbDS Database Updates\Database Updates.gdb\UnmatchedMultiplePipes_All2,fpbFtrID,-1,-1;fpbLong "fpbLong" true false false 8 Double 8 38,First,#,\\fwhqd\home\nordhoka\My Documents\ArcGIS\Projects\fpbDS Database Updates\Database 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"fpbEvMdPAD" true true false 100 Text 0 0 ,First,#,Database Connections\GIS@OFPBDS@NRIMP-DB.sde\ofpbds_gdb.GIS.ofpbds_pt,fpbEvMdPAD,-1,-1;fpbFyTyD "fpbFyTyD" true true false 100 Text 0 0 ,First,#,Database Connections\GIS@OFPBDS@NRIMP-DB.sde\ofpbds_gdb.GIS.ofpbds_pt,fpbFyTyD,-1,-1;fpbOwnTyD "fpbOwnTyD" true true false 100 Text 0 0 ,First,#,Database Connections\GIS@OFPBDS@NRIMP-DB.sde\ofpbds_gdb.GIS.ofpbds_pt,fpbOwnTyD,-1,-1;fpbLOwnTyD "fpbLOwnTyD" true true false 100 Text 0 0 ,First,#,Database Connections\GIS@OFPBDS@NRIMP-DB.sde\ofpbds_gdb.GIS.ofpbds_pt,fpbLOwnTyD,-1,-1;fpbComment "fpbComment" true true false 254 Text 0 0 ,First,#,Database Connections\GIS@OFPBDS@NRIMP-DB.sde\ofpbds_gdb.GIS.ofpbds_pt,fpbComment,-1,-1;fpbStrID "fpbStrID" true true false 13 Text 0 0 ,First,#,Database Connections\GIS@OFPBDS@NRIMP-DB.sde\ofpbds_gdb.GIS.ofpbds_pt,fpbStrID,-1,-1;fpbStrMeas "fpbStrMeas" true true false 8 Double 3 8 ,First,#,Database Connections\GIS@OFPBDS@NRIMP-DB.sde\ofpbds_gdb.GIS.ofpbds_pt,fpbStrMeas,-1,-1;OWEB_status "OWEB Update" true true false 2 Short 0 0 ,First,#,Database Connections\GIS@OFPBDS@NRIMP-DB.sde\ofpbds_gdb.GIS.ofpbds_pt,OWEB_status,-1,-1;OWEB_userid "OWEB_userid" true true false 2 Short 0 5 ,First,#,Database Connections\GIS@OFPBDS@NRIMP-DB.sde\ofpbds_gdb.GIS.ofpbds_pt,OWEB_userid,-1,-1;GlobalID "GlobalID" false false false 38 GlobalID 0 0 ,First,#,Database Connections\GIS@OFPBDS@NRIMP-DB.sde\ofpbds_gdb.GIS.ofpbds_pt,GlobalID,-1,-1;PriorityGroup "PriorityGroup" true true false 15 Text 0 0 ,First,#,Database Connections\GIS@OFPBDS@NRIMP-DB.sde\ofpbds_gdb.GIS.ofpbds_pt,PriorityGroup,-1,-1" # FGDC 1.0 FGDC CSDGM Metadata 150000000 5000 Microsoft Windows XP Version 5.1 (Build 2600) Service Pack 3; ESRI ArcCatalog 9.3.1.3000 en The Oregon Fish Passage Barrier Data Standard (OFPBDS) dataset contains barriers to fish passage in Oregon watercourses. Barriers include the following types of natural or artificial structures: bridges, cascades, culverts, dams, debris jams, fords, natural falls, tide gates, and weirs. The OFPBDS dataset does not include structures which are not associated with in-stream features (such as dikes, levees or berms). Barriers are structures which do, or potentially may, impede fish movement and migration. Barriers can be known to cause complete or partial blockage to fish passage, or they can be completely passable, or they may have an unknown passage status. The third publication of the OFPBDS dataset (Version 3) complies with version 1.1 of the data standard. New optional attributes have been added to describe fish passage barrier feature modifications, to describe supplementary information (via a comments field) and also to linear reference the barrier features to the National Hydrography Dataset. Linear referencing attributes for the Pacific Northwest Hydrography have been retained in this version of the publication datasets, however they are no longer part of the data standard and will be removed from the next dataset publication version. Version 3 of the OFPBDS dataset contains over 30,000 barrier features from seventeen separate sources including: Oregon Department of Fish and Wildlife (ODFW), Oregon Department of Transportation (ODOT), Oregon Department of Water Resources (OWRD), Oregon Department of Forestry (ODF), Oregon Watershed Enhancement Board (OWEB), US Bureau of Land Management (BLM), US Forest Service, Nez Perce Tribe, Benton SWCD, Washington county and watershed councils representing the Rogue, Umpqua, Siuslaw, Santiam, Calapooia, Clackamas and Scapoose basins. The Data Steward obtained fish passage barrier data from multiple data originators between 2008 and 2011, collaborated with them to develop inclusion / exclusion criteria and dataset specific crosswalks for converting data from its original data structure to the structure of the OFPBDS. The data were then converted into the OFPBDS format and analyzed for duplication with existing OFPBDS barrier features. Where duplicates were identified, depending upon the scenario, one feature was either chosen over the other or in some cases attributes from different sources are combined. Source information is retained for each feature. The data were then loaded into the OFPBDS database. Barrier features were linear referenced (Framework Hydro only which is outside of the standard) and the corresponding optional attribute elements were populated. The data conversion, duplication reconciliation and linear referencing protocols are documented in the Oregon Fish Passage Barrier Data Management Plan. A separate dataset containing fish passage barrier features that have been completely removed (e.g. dam removals and culvert replacements) will be published simultaneously with version 3 of the OFPBDS dataset. The OFPBDS database does not represent a comprehensive record of fish passage barriers in Oregon. Attributes (including key attributes such as fish passage status) are often incomplete. Consistency in attribution also varies among data originators. Field verification of barrier features and their attributes will be an important component to making this dataset comprehensive, current and accurate. Fish passage status is a key attribute. Many barrier features - including all ODOT barriers - have an unknown passage status. For other features, the passage status may have changed since documented. Note that this metadata file is best viewed in ArcCatalog with the FGDC Classic Stylesheet. Documentation for the OFPBDS can be found online at http://www.oregon.gov/DAS/EISPD/GEO/docs/bioscience/OregonFishPassageBarrierDataStandardv1dot1.pdf. This dataset is ultimately intended to support the need for an accurate, current and complete representation of the fish passage barriers affecting fish migration throughout the state. The Oregon Fish Passage Barrier Data Standard (OFPBDS) will provide a consistent and maintainable structure for both producers and users of fish passage barrier data. Oregon Department of Fish and Wildlife 20110217 Oregon Fish Passage Barriers ofpbds_gdb.SDE.ofpbds_pt vector digital data http://nrimp.dfw.state.or.us/nrimp/default.aspx?pn=fishbarrierdata Version 2 Information on the Oregon Fish Passage Barrier Data Standard can be found online at http://www.oregon.gov/DAS/EISPD/GEO/docs/bioscience/OregonFishPassageBarrierDataStandardv1dot1.pdf publication date 20110217 In work Continually -124.776293 -116.523447 46.259010 41.923154 229230.396982 2319399.624344 89389.582349 1643769.676837 None fish passage barriers barriers dams culverts tide gates bridges fords water diversions weirs falls cascades fish passage None Oregon OR Pacific Northwest biota environment geoscientificInformation ISO 19115 Topic Category inlandWaters None. See Distribution Liability. SDE Feature Class Oregon Department of Fish and Wildlife Jon Bowers GIS Coordinator mailing and physical address
3406 Cherry Avenue NE
Salem Oregon 97303 United States 503-947-6097 jon.k.bowers@state.or.us Unclassified Barrier features originate primarily from the following agencies: Oregon Department of Fish and Wildlife, Oregon Department of Transportation, Oregon Department of Water Resources, Oregon Department of Forestry, Oregon Watershed Enhancement Board, US Bureau of Land Management, US Forest Service, Nez Perce Tribe, Benton SWCD, Washington County and watershed councils representing the Rogue, Umpqua, Siuslaw, Santiam, Calapooia, Clackamas and Scapoose basins. Oregon Dept. of Fish and Wildlife 3/2010 Oregon Fish Habitat Distribution Data http://nrimp.dfw.state.or.us/nrimp/default.aspx?pn=fishdistdata Oregon Department of Fish and Wildlife 2/2011 Oregon Fish Passage Barriers - Removed and Replaced Features version 2 http://nrimp.dfw.state.or.us/nrimp/default.aspx?pn=fishbarrierdata Version 6.2 (Build 9200) ; Esri ArcGIS 10.7.1.11595 ofpbds_pt vector digital data 2020-05-28T00:00:00 Jon Bowers Oregon Dept. of Fish and Wildlife GIS Coordinator Jon Bowers 4034 Fairview Industrial Dr SE Salem Oregon 97302 jon.k.bowers@state.or.us 503-947-6097 -124.778532 -116.521365 46.288865 41.921351 1 Barrier features described in this dataset are based on surveys and observations that have been made dating back at least to the 1970's, if not earlier. Data have been compiled and converted into the statewide standard format from 2008 to 2015. 2008-01-01T00:00:00 2015-10-15T00:00:00 -124.776293 -116.523447 46.25901 41.923154 1 002 002 This dataset is ultimately intended to support the need for an accurate, current and complete representation of the fish passage barriers affecting fish migration throughout the state of Oregon. The OFPBDS database is the most comprehensive compilation of fish passage barrier information in Oregon however, it does NOT represent a complete and current record of every fish passage barrier within the state. Efforts to address deficiencies in data currency, completeness and accuracy are ongoing. The Oregon Fish Passage Barrier Data Standard (OFPBDS) provides a consistent and maintainable structure for both producers and users of fish passage barrier data. <DIV STYLE="text-align:Left;"><DIV><DIV><P><SPAN>The Oregon Fish Passage Barrier Data Standard (OFPBDS) dataset contains barriers to fish passage in Oregon watercourses. Barriers include the following types of natural or artificial structures: bridges, cascades, culverts, dams, debris jams, fords, natural falls, tide gates, and weirs. The OFPBDS dataset does not include structures which are not associated with in-stream features (such as dikes, levees or berms). Barriers are structures which do, or potentially may, impede fish movement and migration. Barriers can be known to cause complete or partial blockage to fish passage, or they can be completely passable, or they may have an unknown passage status. This dataset complies with version 1.1 of the OFBPDS data standard. New optional attributes have been added to describe fish passage barrier feature modifications, to describe supplementary information (via a comments field) and also to linear reference the barrier features to the National Hydrography Dataset. The OFPBDS dataset now contains over 40,000 barrier features from 19 separate sources including: Oregon Department of Fish and Wildlife (ODFW), Oregon Department of Transportation (ODOT), Oregon Department of Water Resources (OWRD), Oregon Department of Forestry (ODF), Oregon Watershed Enhancement Board (OWEB), Oregon Department of Land Conservation and Development (DLCD) US Bureau of Land Management (BLM), US Forest Service, Nez Perce Tribe, Benton SWCD, Washington county, Lower Columbia River Estuary Partnership and watershed councils representing the Rogue, Umpqua, Siuslaw, Santiam, Calapooia, Clackamas and Scapoose basins. The Data Steward obtained fish passage barrier data from multiple data originators between 2008 and 2019, collaborated with them to develop inclusion / exclusion criteria and dataset specific crosswalks for converting data from its original data structure to the structure of the OFPBDS. The data were then converted into the OFPBDS format and analyzed for duplication with existing OFPBDS barrier features. Where duplicates were identified, depending upon the scenario, one feature was either chosen over the other or in some cases attributes from different sources are combined. Source information is retained for each feature. The data were then loaded into the OFPBDS database. Barrier features were linear referenced (Framework Hydro only which is outside of the standard) and the corresponding optional attribute elements were populated. The data conversion, duplication reconciliation and linear referencing protocols are documented in the Oregon Fish Passage Barrier Data Management Plan. A separate dataset containing fish passage barrier features that have been completely removed or replaced (e.g. dam removals and culvert replacements) is published simultaneously with the OFPBDS dataset. The OFPBDS database is the most comprehensive compilation of fish passage barrier information in Oregon however, it does NOT represent a complete and current record of every fish passage barrier within the state. Efforts to address deficiencies in data currency, completeness and accuracy are ongoing and are often limited by lack of sufficient resources. Attributes (including key attributes such as fish passage status) are often unknown or incomplete. Consistency in attribution also varies among data originators. Field verification of barrier features and their attributes will be an important component to making this dataset current, comprehensive and accurate. Fish passage status is a key attribute. Many barrier features have an unknown passage status. For other features, the passage status may have changed since it was originally documented. Note that this metadata file is best viewed in ArcCatalog. Documentation for the OFPBDS can be found online at http://www.oregon.gov/DAS/EISPD/GEO/docs/bioscience/OregonFishPassageBarrierDataStandardv1dot1.pdf.</SPAN></P></DIV></DIV></DIV> Barrier features originate primarily from the following agencies: Oregon Department of Fish and Wildlife (ODFW), Oregon Department of Transportation (ODOT), Oregon Department of Water Resources (OWRD), Oregon Department of Forestry (ODF), Oregon Watershed Enhancement Board (OWEB), Oregon Department of Land Conservation and Development (DLCD) US Bureau of Land Management (BLM), US Forest Service, Nez Perce Tribe, Benton SWCD, Washington county, Lower Columbia River Estuary Partnership and watershed councils representing the Rogue, Umpqua, Siuslaw, Santiam, Calapooia, Clackamas and Scapoose basins. fish passage barriers barriers dams culverts tide gates bridges fords water diversions weirs falls cascades fish passage biota environment geoscientificInformation inlandWaters <DIV STYLE="text-align:Left;"><DIV><DIV><DIV STYLE="font-size:12pt"><P><SPAN>Notification of any errors would be appreciated please email: jon.k.bowers@state.or.us. The Oregon Department of Fish and Wildlife shall not be held liable for improper or incorrect use of the data described and/or contained herein. Oregon Department of Fish and Wildlife shall be acknowledged as data contributors to any reports or other products derived from these data. This spatial data layer was developed based on a variety of sources. Care was taken in the creation of this layer, but it is provided "as is." The Oregon Department of Fish and Wildlife cannot accept any responsibility for errors, omissions, or positional accuracy in the digital data or underlying records. There are no warranties, expressed or implied, including the warranty of merchantability or fitness for a particular purpose, accompanying any of these products.</SPAN></P></DIV></DIV></DIV></DIV> Jon Bowers Oregon Dept. of Fish and Wildlife GIS Coordinator Jon Bowers 4034 Fairview Industrial Dr SE Salem Oregon 97302 jon.k.bowers@state.or.us 503-947-6097 Jon Bowers Jon Bowers Oregon Dept. of Fish and Wildlife GIS Coordinator Jon Bowers 4034 Fairview Industrial Dr SE Salem Oregon 97302 jon.k.bowers@state.or.us 503-947-6097 Jon Bowers Oregon Metadata Keyword Thesaurus Bioscience, Fish, Anadromous fish, Anadromous fish habitat Oregon Metadata Keyword Thesaurus Oregon en FGDC Content Standards for Digital Geospatial Metadata FGDC-STD-001-1998 local time Jon Bowers Oregon Department of Fish and Wildlife mailing and physical address Salem Oregon 97303
3406 Cherry Avenue NE
United States 503-947-6097 GIS Coordinator jon.k.bowers@state.or.us 20110217 Unclassified None. ArcGIS Metadata 1.0 dataset Downloadable Data Oregon Department of Fish and Wildlife Jon Bowers GIS Coordinator 503-947-6097 jon.k.bowers@state.or.us mailing and physical address
3406 Cherry Avenue NE
Salem Oregon 97303 United States No warranty expressed or implied is made regarding the accuracy or utility of the data on any other system or for general or scientific purposes, nor shall the act of distribution constitute any such warranty. This disclaimer applies both to individual use of the data and aggregate use with other data. It is also strongly recommended that careful attention be paid to the contents of the metadata file associated with these data. Neither the Data Steward nor the data originators shall be held liable for improper or incorrect use of the data described and/or contained herein. 20110217 none Download from http://nrimp.dfw.state.or.us/nrimp/default.aspx?pn=fishbarrierdata https://nrimp.dfw.state.or.us/DataClearinghouse/default.aspx?p=202&XMLname=44.xml File Geodatabase 10.2.2 Jon Bowers Oregon Dept. of Fish and Wildlife GIS Coordinator Jon Bowers 4034 Fairview Industrial Dr Salem Oregon 97302 jon.k.bowers@state.or.us 503-947-6097 File Geodatabase 10.2.2 Vector Simple FALSE 0 TRUE FALSE GCS_North_American_1983 NAD_1983_Oregon_Statewide_Lambert_Feet_Intl coordinate pair international feet 0.000328 0.000328 North American Datum of 1983 Geodetic Reference System 80 6378137.000000 298.257222 Explicit elevation coordinate included with horizontal coordinates 1.000000 NAD_1983_Oregon_Statewide_Lambert_Feet_Intl EPSG 8.9.3(9.0.0) 0 ofpbds_pt Feature Class 0 Fish passage barrier points OFPBDS OBJECTID OBJECTID OID 4 0 0 Internal feature number. ESRI Sequential unique whole numbers that are automatically generated. fpbFtrID fpbFtrID Integer 4 0 0 Framework unique identifier for the fish passage barrier feature (generated by the Horizontal Steward) OFPBDS Sequential unique whole numbers that are generated by the Data Steward. fpbLong fpbLong Double 8 0 0 Longitudinal planar component of point location on earth's surface, in geographic decimal degrees NAD83 OFPBDS fpbLat fpbLat Double 8 0 0 Latitudinal planar component of point location on earth's surface, in geographic decimal degrees NAD83 OFPBDS fpbSiteID fpbSiteID Integer 4 0 0 Framework unique identifier for the fish passage barrier site (generated by the Horizontal Steward) OFPBDS Sequential unique whole numbers that are generated by the Data Steward. fpbRevDt fpbRevDt String 8 0 0 Date of data entry into or revision in the Framework dataset (YYYYMMDD) OFPBDS fpbOFtrID fpbOFtrID String 40 0 0 Unique ID for each fish passage barrier feature at a site, generated by the data originator OFPBDS fpbONm fpbONm String 30 0 0 Name of the source originator / entity that provides the data OFPBDS fpbOSiteID fpbOSiteID String 40 0 0 OFPBDS Unique ID for each fish passage barrier site, generated by the data originator fpbLocMd fpbLocMd String 15 0 0 Method used to collect or generate location information OFPBDS FieldGPS Field - GPS OFPBDS FieldQuad Field - Record location on 7.5' quad map OFPBDS FieldOther Field - other OFPBDS DigDerive Digitally derived (e.g. located on-screen using DOQ or DRG) OFPBDS ExtInv External inventory (e.g. National Inventory of Dams, GNIS) OFPBDS ProfJudge Located on map via professional judgement (first-hand knowledge of feature location) OFPBDS Other Other OFPBDS Unknown Unknown OFPBDS fpbLocAccu fpbLocAccu SmallInteger 2 0 0 Accuracy of fish passage barrier feature location (+ or - feet) OFPBDS 9999 Unknown OFPBDS fpbLocDt fpbLocDt String 8 0 0 OFPBDS Most recent date of location data collection (YYYYMMDD) fpbFtrTy fpbFtrTy String 25 0 0 Fish passage barrier feature type OFPBDS Dam Dam OFPBDS Culvert Culvert - road stream crossing OFPBDS WeirSill Weir / sill OFPBDS Falls Falls OFPBDS CascadeGradientVelocity Cascades / gradient / velocity (including debris torrented reaches) OFPBDS TideGate Tide gate OFPBDS Bridge Bridge - road stream crossing OFPBDS Ford Ford - road stream crossing OFPBDS Other Other known fish passage barrier feature including debris jams OFPBDS Unknown Unknown OFPBDS fpbFtrNm fpbFtrNm String 50 0 0 Fish passage barrier feature name OFPBDS fpbRmvDt fpbRmvDt String 8 0 0 Date that fish passage barrier feature was removed (required only if removed - YYYYMMDD) OFPBDS fpbMltFtr fpbMltFtr String 7 0 0 Flag for multiple fish passage barrier features at the site OFPBDS yes yes (multiple fish passage barrier features exist at the site AND features are records in the OFPBDS database) OFPBDS no no OFPBDS unknown unknown OFPBDS fpbFPasSta fpbFPasSta String 8 0 0 Status of fish passage at the barrier feature OFPBDS Blocked Not passable OFPBDS Partial Partially passable - a barrier to at least some fish at some time OFPBDS Passable Completely passable OFPBDS Unknown Unknown OFPBDS UnkAnad Unknown passage within the range of anadromy OFPBDS fpbStaEvDt fpbStaEvDt String 8 0 0 Date passage status was last evaluated (YYYYMMDD) OFPBDS fpbStaEvMd fpbStaEvMd String 20 0 0 Passage status evaluation method OFPBDS USFSBLMFullAssess USFS / BLM full passage assessment (e.g. FishXing) OFPBDS OtherFullAssess Other full passage assessment OFPBDS USFSBLMPartialAssess USFS / BLM partial passage assessment (coarse screen filter) OFPBDS OtherPartialAssess Other partial passage assessment (including professional judgement) OFPBDS ByDesign By evaluation of design plans OFPBDS Unknown Unknown OFPBDS NA Not applicable - use NA where fish passage status is unknown OFPBDS fpbFySta fpbFySta String 20 0 0 Fishway status OFPBDS FuncOkay Functioning, passes fish OFPBDS NeedsMaint Not properly functioning, needs repair or maintenance OFPBDS Abandoned Abandoned fishway - no longer needed (e.g. fishway at natural falls) OFPBDS None No fishway OFPBDS NoneMitigation No fishway - mitigation provided OFPBDS NoneExempt No fishway - negligible current benefit OFPBFDS NoneConflict Fishway not wanted - conflicts with other native fish management needs OFPBDS Unknown Unknown OFPBDS Shape Shape Geometry 0 0 0 Feature geometry. ESRI Coordinates defining the features. fpbFyCrit fpbFyCrit String 7 0 0 Flag for whether fishway meets passage criteria yes fishway meets passage criteria OFPBDS no fishway does not meet passage criteria OFPBDS unknown Unknown whether fishway meets passage criteria OFPBDS OFPBDS fpbCrdDesc fpbCrdDesc String 254 0 0 Identifies exact location to which coordinates refer OFPBDS Permanent_Identifier Permanent_Identifier String 40 0 0 Barrier feature event record permanent ID (GUID) Maintained by the Hydrography Event Mgt Tools (HEM). OFPBDS GUID values ReachCode ReachCode String 14 0 0 ReachCode value for the NHD Flowline record that the event record references. Maintained by the HEM tools. OFPBDS Unique to NHD Flowline reaches Measure Measure Double 8 0 0 Measure along the NHD Flowline record where the event record is located. Maintained by the HEM tools 0 100 EventDate EventDate Date 8 0 0 The date the event record was created or last modified. Maintained by the HEM tools OFPBDS ReachSMDate ReachSMDate Date 8 0 0 Reach spatial modification date. Maintained by the HEM tools. OFPBDS ReachResolution ReachResolution SmallInteger 2 0 0 The resolution of the NHD source data. OFPBDS fpbStrID fpbStrID String 13 0 0 Stream route identifier (Framework Hydrography) OFPBDS fpbStrMeas fpbStrMeas Double 8 0 0 Framework stream route measure (kilometers to 3 decimal places) OFPBDS fpbRdMile fpbRdMile Double 8 0 0 Field measurement of road mile point OFPBDS fpbStrNm fpbStrNm String 50 0 0 Stream name from GNIS OFPBDS fpbLocONm fpbLocONm String 30 0 0 Location data provider entity (if different from identification data originator). OFPBDS fpbRdID fpbRdID String 13 0 0 Road route identifier (Framework - OR Road Centerline) OFPBDS fpbRdNm fpbRdNm String 50 0 0 Road name from GNIS OFPBDS fpbFtrSTy fpbFtrSTy String 30 0 0 Fish passage barrier feature subtype OFPBDS [Dam] DamPermanent Dam that is permanent throughout the year OFPBDS [Dam] DamSeasonal Dam that is in place for only part of the year OFPBDS [Culvert] OpenArch Open arch OFPBDS [Culvert] OpenBox Open box OFPBDS [Culvert] Round Round OFPBDS [Culvert] PipeArch Pipe arch OFPBDS [Culvert] Full Box Full box OFPBDS [Culvert] Other Other known culvert shape OFPBDS [Culvert] Unknown Unknown OFPBDS [TideGate] SideHingedAluminum Side-hinged orientation, aluminum material, not mechanically controlled OFPBDS [TideGate] TopHingedIronSteel Top-hinged orientation, iron or steel material, not mechanically controlled OFPBDS [TideGate] TopHingedWood Top-hinged orientation, wood material, not mechanically controlled OFPBDS [TideGate] MechanicallyControlled Mechanically controlled OFPBDS [TideGate] Other Other known tide gate hinge-orientation, material or controls OFPBDS [TideGate] Unknown Unknown OFPBDS [Ford] Concrete Concrete OFPBDS [Ford] Asphalt Asphalt OFPBDS [Ford] NativeMaterial On-site, native material OFPBDS [Ford] Off-site rock Off-site rock OFPBDS [Ford] Other Other known surface material OFPBDS [Ford] Unknown Unknown OFPBDS fpbFtrNmSr fpbFtrNmSr String 5 0 0 Fish passage barrier feature name source OFPBDS GNIS GNIS OFPBDS other other OFPBDS fpbHeight fpbHeight Single 4 0 0 Fish passage barrier feature height (feet, 1 decimal) OFPBDS fpbLength fpbLength Single 4 0 0 Fish passage barrier feature length (feet, 1 decimal); distance is the measure between the furthest upstream and furthest downstream parts of the feature OFPBDS fpbWidth fpbWidth Single 4 0 0 Fish passage barrier feature width (feet, 1 decimal); distance is the measure between stream banks (includes dam crest length) OFPBDS fpbSlope fpbSlope Single 4 0 0 Slope of fish passage barrier feature (percent, 1 decimal); zero value represents flat surface (as opposed to no data) OFPBDS fpbDrop fpbDrop Single 4 0 0 Distance from culvert outlet to the water surface of the pool below (feet, 1 decimal); zero value represents no drop (as opposed to no data) OFPBDS fpbModTy fpbModTy String 10 0 0 Baffles Feature added to a culvert to increase the hydraulic roughness OFPBDS StreamSim A channel that simulates characteristics of the adjacent natural stream channel OFPBDS Weirs Feature built across a stream to raise its level OFPBDS Other Other fish passage barrier modification to improve passage OFPBDS Unknown Unknown modification type OFPBDS Fish passage barrier feature modification type OFPBDS fpbModDesc fpbModDesc String 254 0 0 Fish passage barrier feature modification description OFPBDS fpbOrYr fpbOrYr String 4 0 0 The year the fish passage barrier feature was built or installed (origin year). Natural barriers to be assigned year of statehood (1859) unless known to be otherwise. OFPBDS fpbModDt fpbModDt String 8 0 0 Fish passage barrier feature modification date (YYYYMMDD) OFPBDS fpbDesONm fpbDesONm String 30 0 0 Name of description data originator / entity (if different from identification data originator) OFPBDS fpbOwn fpbOwn String 60 0 0 Owner of the fish passage barrier feature OFPBDS fpbLOwn fpbLOwn String 60 0 0 Owner of the land where the fish passage barrier feature is located OFPBDS fpbOperate fpbOperate String 60 0 0 Operator of the fish passage barrier feature OFPBDS fpbFyOwn fpbFyOwn String 60 0 0 Fishway owner OFPBDS fpbOwnTy fpbOwnTy String 15 0 0 Fish passage barrier feature owner type OFPBDS Federal Federal OFPBDS State State OFPBDS Tribal Tribal OFPBDS Private Private OFPBDS PubUtility Public Utility OFPBDS PubSpDistrict Special district - water control, irrigation, drainage OFPBDS County County OFPBDS City City OFPBDS Other Other OFPBDS fpbLOwnTy fpbLOwnTy String 15 0 0 Fish passage barrier feature landowner type OFPBDS Federal Federal OFPBDS State State OFPBDS Tribal Tribal OFPBDS Private Private OFPBDS PubUtility Public Utility OFPBDS PubSpDistrict Special district - water control, irrigation, drainage OFPBDS County County OFPBDS City City OFPBDS Other Other OFPBDS fpbOwnONm fpbOwnONm String 30 0 0 Name of ownership data originator / entity (if different from identification data originator) OFPBDS fpbFyTy fpbFyTy String 15 0 0 Fishway type OFPBDS Pool Pool style fishways have a series of distinct pools in which the energy of the flow entering each one is entirely dissipated prior to flowing to the next OFPBDS BaffledChute Chutes or flumes with roughness, designed to reduce velocity, allowing fish passage OFPBDS Hybrid Combination of multiple fishway types OFPBDS FullSpanning A fishway that crosses the entire stream channel OFPBDS Trap Structures that direct the stream flow to attract upstream migrants into holding (impoundment) areas OFPBDS Other Other known fishway type OFPBDS Unknown Unknown fishway type OFPBDS fpbFySTy fpbFySTy String 20 0 0 Fishway subtype OFPBDS [Pool] PoolVertSlot Vertical slot OFPBDS [Pool] PoolAndWeir Pool and weir OFPBDS [Pool] PoolWeirOrifice Weir and orifice OFPBDS [Pool] PoolSecChan Engineered secondary channel OFPBDS [Pool] PoolOther Pool - other OFPBDS [BaffledChute] BChuteAKSteep Alaska Steeppass OFPBDS [BaffledChute] BChuteDenil Denil OFPBDS [BaffledChute] BChuteSecChan Engineered secondary channel OFPBDS [BaffledChute] BChuteOther Baffled chute - other OFPBDS [Hybrid] HybridPoolChute Pool and chute OFPBDS [Hybrid] HybridSecChan Engineered secondary channel OFPBDS [Hybrid] HybridOther Hybrid - other OFPBDS [FullSpanning] FlSpanRockWeir Rock weirs OFPBDS [FullSpanning] FlSpanLogWeir Log weirs OFPBDS [FullSpanning] FlSpanConcreteWeir Concrete weirs OFPBDS [FullSpanning] FlSpanOtherWeir Full spanning - other weirs OFPBDS [FullSpanning] FlSpanRoughChan Roughened channel OFPBDS [FullSpanning] FlSpanHybridChan Hybrid channel OFPBDS [FullSpanning] FlSpanOtherChan Full spanning - other channel OFPBDS [Trap] TrapPass Trap and pass - includes mechanical lifts / locks OFPBDS [Trap] TrapHaul Trap and haul OFPBDS fpbFyOrYr fpbFyOrYr String 4 0 0 The year the fishway was built or installed (origin year) OFPBDS fpbFPasONm fpbFPasONm String 30 0 0 Name of fish passage data originator / entity (if different from identification data originator) OFPBDS fpbLocMdD fpbLocMdD String 100 0 0 Fish passage barrier feature location collection method - description for "other" OFPBDS fpbFtrTyD fpbFtrTyD String 100 0 0 Fish passage barrier feature type - description for "other" OFPBDS fpbFtrSTyD fpbFtrSTyD String 100 0 0 Fish passage barrier feature subtype - description for "other" OFPBDS fpbEvMdFAD fpbEvMdFAD String 100 0 0 Fish passage status evaluation method - description for "other full assessment" OFPBDS fpbOwnTyD fpbOwnTyD String 100 0 0 Barrier feature owner type - description for other OFPBDS fpbEvMdPAD fpbEvMdPAD String 100 0 0 OFPBDS Fish passage status evaluation method - description for "other partial assessment" fpbComment fpbComment String 254 0 0 Additional, relevant information about the fish passage barrier feature OFPBDS fpbFyTyD fpbFyTyD String 100 0 0 Fishway type - description for "other" OFPBDS OWEB_status OWEB Update SmallInteger 2 0 0 Status of OWEB records as they are added to the database via the OWRI application. OWEB fpbLOwnTyD fpbLOwnTyD String 100 0 0 Fish passage barrier feature landowner type - description for "other" OFPBDS OWEB_userid OWEB_userid SmallInteger 2 0 0 Field for tracking OWEB applicants who provide input into the OFPBDS database. OWEB GlobalID GlobalID GlobalID 38 0 0 PriorityGroup PriorityGroup String 15 0 0 Ranking of high priority fish passage barriers based on a K-means cluster analysis to partition the data into the respective groupings from top ten to group 16. 2019 priority list methods paper Detailed information for the Oregon Fish Passage Barrier Data Standard can be found online at http://www.oregon.gov/DAS/EISPD/GEO/docs/bioscience/OregonFishPassageBarrierDataStandardv1dot1.pdf Detailed information for the OFPBDS feature attributes can be found online at http://www.oregon.gov/DAS/EISPD/GEO/docs/bioscience/OregonFishPassageBarrierDataStandardv1dot1.pdf 20230602 Oregon Department of Fish and Wildlife Jon Bowers GIS Coordinator mailing and physical address
3406 Cherry Avenue NE
Salem Oregon 97303 United States 503-947-6097 jon.k.bowers@state.or.us Compiled fish passage barrier data from multiple agencies, counties, watershed councils and one tribe into the Oregon Fish Passage Barrier Data Standard (OFPBDS) geodatabase. In compiling fish passage barrier features from the different data originators into the OFPBDS database, the Data Steward followed some general guidelines: 1. Identify and acquire data and metadata. 2. Data Discovery. Review metadata to ensure an understanding of the data; its primary content, characteristics, capabilities and limitations. Develop key questions of usability for purposes of meeting the requirements of the standard, especially related to unique IDs, location, barrier type and passage status. 3. Consult with originator to answer questions and resolve outstanding issues (e.g. persistent unique IDs) for meeting the requirements of the standard. 4. Determine appropriate subset to incorporate, if any, based on presence of location data, unique IDs, specific attribution (e.g., exclude cross drain culverts - culverts not on stream crossings). 5. Develop a proposed methodology for converting the data into the OFPBDS format. Seek input and approval from the data originator for the data conversion methodology. Address issues as necessary so there is agreement on the methodology. 6. Process the data into the standard format. 7. Perform quality assurance routines to ensure that the data have been converted to the standardized format according to plan. 8. Analyze the data to determine whether there are duplicate barrier records coming from multiple sources. Address duplicate records according to established protocols that are found in the Barrier Data Management Plan. 9. Linear reference barrier features. 10. Reconcile barrier data with the Oregon Watershed Restoration Inventory. 11. Document data processing steps. 12. Load the data into the OFPBDS geodatabase. The steps outllined above were used by the Data Steward to standardize barrier data from the multiple sources that were compiled and integrated. The process by which data were converted into the OFPBDS format and loaded into the OFPBDS database required collaboration with the data originators and the development of numerous record selection methodologies, attribute crosswalks, decision trees, issue resolutions, and data management protocols. Common difficulties included ensuring that all records from a given originator had a unique originator feature identifier (fpbOFtrID) and determining how to crosswalk various criteria used for assessing fish passage status. If requested, more detailed metadata on the standardization of barrier data can be provided. ESRI ArcInfo 9.3.1 2009 - 2011 Oregon Department of Fish and Wildlife Jon Bowers GIS Coordinator mailing and physical address
3406 Cherry Avenue NE
Salem Oregon 97303 United States 503-947-6097 jon.k.bowers@state.or.us Converted Oregon Department of Fish and Wildlife (ODFW) fish passage barrier data into the Oregon Fish Passage Barrier Data Standard (OFPBDS) format and loaded the data into the OFPBDS geodatabase. Metadata for ODFW barrier data states the following: This dataset contains barriers to fish passage that are known to affect and potentially affect anadromous and/or resident fish migration within the state of Oregon. The following barrier types are included: dams, culverts, falls, cascade/gradient/velocity, hatchery facility-related, tide gates, debris jams, water diversions, insufficient flow, fords, bridges and weirs. The passage status attribute describes whether a barrier feature blocks passage (complete or partial blockage), is passable or has an unknown passage status. The passage status attribute, in some cases, may not reflect the current passage status of the barrier (for culverts in particular) as conditions may have changed since the date the passage status was last evaluated. The passage status for many of the barriers is unknown due to potential effects on species and/or life stages where little information exists at this time. Consequently, many of these barriers may be completely passable to most if not all the species and life stages that have a need to migrate through the affected stream reach. The dataset includes the ODFW - ODOT jointly developed "Assessment of Road Culverts for Fish Passage Problems on State and County Owned Roads" (1999). ODFW barrier data exist in an enterprise geodatabase consisting of multiple tables and one point feature class. The data were exported in June 2009 into a replica copy of the enterprise geodatabase where the records were manipulated. OFPBDS fields were added to the database. A crosswalk between ODFW and OFPBDS attributes and attribute values was developed. Once the crosswalk was completed, attribute values for all the point features were populated in the OFPBDS fields. The point features and attributes were then loaded into the OFPBDS geodatabase. A number of ODFW staff were consulted for the crosswalk. Agency staff were also involved in the standardization process. Specific notes regarding the ODFW data: * The coordinate system of the spatial coordinates in the fpbLong and fpbLat fields is GCS_North_American_1983. * For the multiple features attribute (fpbMltFtr), those records with a "yes" are features which occur at multiple-feature sites AND the features are part of multiple-feature sites which have the multiple features in the OFPBDS database. The fpbMltFtr attribute was not used to indicate features belonging to multiple-feature sites unless records for the features were actually in the database. * ODFW data are linear-referenced to the 1:24,000-scale PNW Framework Hydrography. The stream identifier (fpbStrID), stream measure (fpbStrMeas) and stream name (fpbStrNm) are dervied from the framework hydrography. * Values for road name (fpbRdNm) are what was originally inputted for the ODFW data; the source of the name varies. * A value of 0 for slope (fpbSlope) is presumed to indicate a flat plane. * A value of 0 for drop (fpbDrop) is presumed to indicate no drop. ODFW barrier data are published online at http://nrimp.dfw.state.or.us/nrimp/default.aspx?pn=fishbarrierdata. ESRI ArcInfo 9.3.1 2009 Converted Oregon Department of Transportation (ODOT) culvert data into the Oregon Fish Passage Barrier Data Standard (OFPBDS) format and loaded the data into the OFPBDS geodatabase. Culvert data from ODOT's Drainage Facility Management System (DFMS) were exported into XML format and provided to the Data Steward in August 2009. The data were converted into a feature class based upon the spatial coordinates of the records and added into a geodatabase where the records were manipulated. A methodology was developed to identify which of the ODOT culvert records were culverts at stream crossings. OFPBDS fields were added to the database. A crosswalk between ODOT and OFPBDS attributes and attribute values was developed. Once the crosswalk was completed, attribute values for the selected point features were populated in the OFPBDS fields. The point features and attributes were then loaded into the OFPBDS geodatabase. Several ODOT staff were consulted for the crosswalk and the record selection methodology. Specific notes regarding the ODOT data: * The coordinate system of the spatial coordinates in the fpbLong and fpbLat fields is GCS_North_American_1983. * Features with a originator feature identifier (fpbOFtrID) beginning with "T" are temporary records and are (eventually) replaced. * Some culverts exist at multiple-feature sites. Since ODOT provided only one record per site for multiple-feature sites, the Data Steward added culvert records for these additional features. * For the multiple features attribute (fpbMltFtr), those records with a "yes" are features which occur at multiple-feature sites AND the features are part of multiple-feature sites which have the multiple features in the OFPBDS database. The fpbMltFtr attribute was not used to indicate features belonging to multiple-feature sites unless records for the features were actually in the database. Fish passage status (fpbFPasSta) for ODOT records has been assigned by ODFW using the following criteria: - where culvert drop > 1 foot and < 3.2 feet, passage status was assigned as "partial" - where culvert drop > 3.2 feet, passage status was assigned as "blocked" Fish passage status for ODOT culverts is a determination made by ODFW staff; ODOT defers to ODFW for evaluating passage status. * Values for stream name (fpbStrNm) were provided by ODOT; the source of the stream name varies. * For the road identifier (fpbRdID) and road measure (fpbRdMeas) attributes, ODOT's Highway and Milepoint attributes were used. Note that these two attributes alone are not enough to identify ODOT road features and their locations - other road attributes are needed as well. Note also that ODOT has more than one type of mileage (example: Milepoint 45 is not the same as Milepoint Z 45). fpbRdMeas is the road route measure in kilometers -- units in Milepoint were converted from miles. * A value of 0 for drop (fpbDrop) is presumed to indicate no drop. ESRI ArcInfo 9.3.1 2009 - 2011 Oregon Department of Fish and Wildlife Jon Bowers GIS Coordinator mailing and physical address
3406 Cherry Avenue NE
Salem Oregon 97303 United States 503-947-6097 jon.k.bowers@state.or.us Oregon Department of Fish and Wildlife Jon Bowers GIS Coordinator mailing and physical address
3406 Cherry Avenue NE
Salem Oregon 97303 United States 503-947-6097 jon.k.bowers@state.or.us Converted US Bureau of Land Management (BLM) data into the Oregon Fish Passage Barrier Data Standard (OFPBDS) format and loaded the data into the OFPBDS geodatabase. Data from six BLM districts in western Oregon were incorporated: Coos Bay, Eugene, Lakeview, Medford, Roseburg, Salem. Eleven BLM datasets were separately added into the OFPBDS geodatabase. BLM data were initially provided to the Data Steward October 2008, the geographic extents of which were typically entire BLM districts or individual resource areas. Subsequently (January - May 2009), the Data Steward obtained data from several BLM districts/resource areas, and this information was used instead of the original files. BLM data were provided in a variety of formats: GIS (shapefiles, geodatabases) and non-GIS (Access databases, Excel spreadsheets, Word documents). Tabular data (non-GIS) included both records with spatial coordinates and records without coordinates. Across BLM, there was a good level of consistency in the datasets, in terms of attributes and point collection. But, there were also substantial differences among the records, requiring that each dataset incorporated into the OFPBDS be handled individually. Not all barrier data provided to the Data Steward made it into the OFPBDS. There are three reasons for this: (a) The records are features, like cross drains (i.e., culverts not on streams), which are not on road-stream crossings. (b) The barriers are road-stream crossings not considered to be fish-bearing. (c) The datasets were provided in a non-GIS format and did not contain spatial coordinates, so the tabular information was not converted into GIS given the time constraints of the project. The overall process for incorporating BLM data into the fish passage barrier data standard was as follows: 1. Obtain BLM data. 2. Develop a crosswalk between BLM and OFPBDS, and develop a methodology to determine which records, if not all, to include in the standard. 3. Address any issues (like unique identifiers). 4. Convert data into the standard. 5. Provide standardized data back to BLM (and often also provide Steward-modified intermediate data developed during standardization, especially where identifiers were manipulated). 6. Throughout the entire process, BLM state and district staff were consulted. The Steward worked with the BLM data "as is". In other words, the Steward did not attempt to review, edit or 'correct' BLM records, locations or attributes. The goal was to get as much information into the standard as possible. Most BLM barrier data contain attributes which match those in the standard as well as attributes which do not exist in the standard. Throughout the process of converting BLM data into the OFPBDS, a series of determinations, assumptions and decisions were made. A BLM - OFPBDS Crosswalk (spreadsheet) was developed and contains a record of this, along with a document detailing key GIS steps in the conversion process. In order to standardize the data, crosswalks of each BLM dataset were developed to ensure that attributes and attribute values were properly matched. The crosswalk details how barriers were converted into the OFPBDS format. Two issues highlight the difficulty in integrating the data: unique identifiers (IDs); standardizing attribute values for fish passage status. There were several problems related to BLM records containing unique originator identifiers (IDs): a. There was not a consistent, unique identifier for barrier records among BLM districts and resource areas. b. Some BLM datasets did not contain any ID at all. c. Some BLM datasets contained records with duplicated IDs. To address these problems, the Steward developed a system whereby a prefix (e.g., "BLMMed" for BLM - Medford District) was added to the ID provided by BLM, or if there was no unqiue ID, the ID was modified or generated by the Steward. As for fish passage status, the OFPBDS considers barriers to be Blocked (not passable), Partial (partially passable), Passable, or Unknown. Where passage status was indicated, BLM data utilized several criteria/definitions: a. professional judgment, b. culvert design criteria, c. coarse screen filter (Green, Grey, Red). Crosswalking passage status can be less than exact (e.g where a coarse screen filter result = Red that could either equate to a partial or completely blocked culvert. In version 3 of the OFPBDS published dataset, BLM data based on a coarse screen filter result of red have been reclassified with a passage status of "partial" with the exception of culverts with drops > 3.2 feet which had a passage status of "blocked" maintained. Specific notes regarding the BLM data (for all source datasets): * The coordinate system of the spatial coordinates in the fpbLong and fpbLat fields is GCS_North_American_1983. * Most BLM datasets included BLM and non-BLM 'culverts', especially private barriers. * Values for road name (fpbRdNm) were provided by BLM, and tended to reflect BLM's internal road IDs. * Values for stream name (fpbStrNm) were provided by BLM; the source of the stream name varies. Specific notes regarding the BLM data (for one - or more - source datasets): * For fish passage status (fpbFPasSta), some BLM datasets utilized a BLM coarse filter to assess passage status while other BLM datasets utilized culvert design specifications ('Fish Pass'). The following represents how these attribute values were crosswalked to the OFPBDS values: BLM Coarse Filter OFPBDS Green Passable Grey Unknown Red Blocked BLM 'Fish Pass' OFPBDS Yes Passable No Blocked ESRI ArcInfo 9.3.1 2009 - 2011 Oregon Department of Fish and Wildlife Jon Bowers GIS Coordinator mailing and physical address
3406 Cherry Avenue NE
Salem Oregon 97303 United States 503-947-6097 jon.k.bowers@state.or.us Reconciled barrier features duplicated in the Oregon Fish Passage Barrier Data Standard (OFPBDS) geodatabase. Duplication Analysis Phase The Duplication Analysis phase consists of a set of procedures to determine if duplication exists between the targeted data and the OFPBDS. The Duplication Analysis occurs after the crosswalk methodology is approved, and the data is converted accordingly. Proximity is the most effective indicator in determining duplication, followed by a thorough, manual quality assurance review by GIS Analyst that considers attribute values and other factors such as data currency and completeness of the source datasets. The Duplication Analysis processing steps are as follows: 1) Build a Workstation (MXD): Using ArcMap, create a MXD (Map document) to house all of the data necessary to perform the Duplication Analysis. A group of datasets are required for the proximity analysis (model), and manual analysis (basemap data). a) Model Datasets: The three datasets required to run the duplication analysis model include: (1) Targeted Barriers, (2) OFPBDS, and a (3) Study Area. The targeted barriers are barriers of interest scheduled to be added to the standard, and the OFPBDS is the most recent updated version of the standard. The Study area is a polygon file that completely surrounds the targeted barriers, and can either be generated from hydrologic unit codes, or any boundary data that encompasses all targeted barriers. It is recommended to make addition modifications to the study area to tightly encompass the targeted barriers. b) Manual Datasets: The datasets instrumental in the manual analysis include: Streams (complete watercourse layer), roads (combination of BLM highways and roads), Image Web Server (Oregon Explorer), ESRI Topography (ESRI Map Server), ESRI Imagery World 2D (ESRI Map Server). These basemap datasets assist in determining apparent or ‘potential’ barrier locations. For instance, the barriers of concern for these efforts are on fish bearing streams, and in most cases, at the intersections of roads and streams. The two sets of satellite imagery shares a number of aerial indicators including: roads, streams, drainages, pools, linear vegetation indicating streams, infrastructure, and even the barriers themselves. The Topography layer helps identify slope, aspect, drainages, infrastructure, streams, roads and elevation. All together, these datasets present a strong representation of where barriers are ‘most likely’ located. 2) Run the Model: The Duplication Analysis Model (DAM) is designed to assist in the identification of duplication between barriers scheduled for integration in to the OFPBDS, and barriers that already exist in the OFPBDS. The primary goal of DAM is to distinguish between unlikely and potential duplicates in the Targeted Barriers. The unlikely duplicate barriers will be directly integrated in to the OFPBDS; where as the potential duplicates will require further investigation and analysis. a) DAM Parameters: There are three model parameters necessary to execute DAM indicated by a blue oval. These parameters include the Targeted Barriers, the OFPBDS dataset, and the custom Study Area. b) Model Assumptions / Limitations: The DAM does pose some limitations and assumptions that need to be addressed. 1) Assumption 1: DAM classifies duplicates automatically as a standalone tool. DAM is not the sole tool to identify duplication; its intention is to assist the GIS Analyst in the Duplication Analysis Process by providing a platform for further analysis with enhanced capabilities (filtered datasets, UIDs, relationship and connectivity potential, and distance measurements). 2) Assumption 2: The datasets (OFPBDS & Target Barriers) are geographically accurate. There may be unique instances where barrier features are not accurate, resulting in a false duplicate, or no duplicate at all. The Analyst Duplication Assessment will legitimize these features based upon attribute comparison, if their identified as a duplicate feature. 3) Assumption 3: The closest feature from the Target Barrier is a duplicate. In some cases, there is a duplicate, while in others there may not be. If there is a duplicate, it’s not always the closest barrier. The Model was designed to accommodate this situation, by clipping all features within 150 meters of the features as a base to run the Near Analysis. The Analyst Duplication Assessment would pick up these instances based on attribute comparison, geospatial patterns, and remote sensing using the available base map data. 4) Limitation 1: Horizontal accuracy of a feature needs to be taken in to account when comparing potential duplicates. For instance, the location accuracy of a feature may be outside of the established potential duplication range of 150 meters. 5) Limitation 2: Potential duplication is derived entirely geospatially using proximity. It does not account for similar or disparate descriptive attribute data to determine potential duplication. c) DAM Operations: There are four geospatial operations within DAM indicated by yellow boxes. First, DAM clips the OFPBDS features to the Study Area (clip). This provides a comprehensive OFPBDS copy to examine in future analysis. Next, DAM designates a 150 meter buffer around the Target Barriers (buffer), and clips the OFPBDS barriers to this buffer layer (clip 2), which results in an OFPBDS_Clipped dataset with only OFPBDS features within 150 meters of the Target Barriers. Finally, DAM performs an analysis on the Target_Barriers by calculating their distance from the closest OFPBDS_Improve barriers (near), and its corresponding ObjectID. The distance and ObjectID are added to two fields in the Target_Barriers. Note* The OFPBDS_Clipped dataset’s name will change to OFPBDS_Improve. This dataset will be used to improve duplicate features which reside in the OFPBDS if more comprehensive or accurate data is available. d) DAM Results: Two significant datasets are produced by DAM that requires further investigation. One is the OFPBDS_Improve, and the second is a revised Target_Barriers. Again, the OFPBDS_Improve dataset are OFPBDS features within 150 meters of the Target_Barriers. The OFPBDS_Improve is a direct result of the second clip operation in DAM. The revised Target_Barriers is the original Target_Barriers layer, although has two new fields added in the attribute table; one is named NEAR_FID, and the other NEAR_DIST. The NEAR_FID houses the ObjectID of the corresponding feature in the OFPBDS. Potentially, the tables can now be internally linked using the Object_ID field in OFPBDS_Improve, and the NEAR_FID field in the Target Barriers. This link may support relationship classes, joins, and several relate functions which can be applied for further evaluation in the manual analyst review. The OFPBDS_Improve dataset will be set aside for further analysis in the manual review. The Target_Barrier dataset can be delineated in to two subtypes. Features inside the 150 meter buffer will be extracted to a subsequent dataset called Potential_Duplicates. Features outside of the buffers range are extracted to a Barrier Final dataset, and set to be integrated to the OFPBDS. 3) Analyst Duplication Assessment: The Analyst Duplication Assessment is designed to physically sift through the Potential Barriers manually and compare their attributes to that of the OFPBDS_Improve. During this stage, it’s imperative to utilize professional judgment, while at all times protecting the integrity of the OFPBDS. The initial approach is to compare these datasets by their proximity to one another, and their descriptive barrier attributes. The Potential_Duplicates dataset is the primary dataset for evaluation in this assessment. a) Data Preparation: Using the workstation set forth in the first process, three main barrier datasets need to be added, and one created. These include the OFPBDS_Improve, Barriers_Final, and Potential_Duplication. An additional empty dataset called Questionable_Duplicates is also needed to house questionable barriers. b) Analyze Barriers: Two primary barrier datasets are necessary at this stage to identify duplication. They include the Apparent_Duplicates and OFPBDS_Improve datasets. By comparing these datasets by their proximity to one another, surrounding infrastructure, topography, vegetation, barrier measurements, hydrology, landscape, road/stream intersections, and remote sensing, a GIS Analyst can determine with a fair amount of certainty whether duplication exists. A document entitled, “Reconciling Duplicated barrier Features among Data Sources in the Oregon Fish Passage Barrier Data Standard” provides some assistance in this process. c) Decision Results: Three actions result from this process, which all derive from the Potential_Duplicates dataset. 1. Duplication is Determined = Data is placed in an Apparent_Duplicate dataset, and set aside for further analysis when comparing the datasets already established in the OFPBDS (OFPBDS_Improve). Refer to the section d of this process. 2. Duplication is Questionable = Record is cut and pasted to the Questionable_Duplicate dataset. (Corresponding Record is removed from OFPBDS_Improve) The Questionable_Duplicate dataset is provided back to their origin source for further analysis. 3. Barrier is Unique = Record is cut and pasted to the Target_Finals. (Corresponding Record is removed from OFPBDS_Improve) The Target_Finals are integrated to the OFPBDS directly upon completion. d) Update OFPBDS: The approach is to improve upon existing data residing in the OFPBDS. If duplication has been determined through the Apparent_Duplicate dataset, the attributes are compared to their corresponding barrier in the OFPBDS. If data is superior in the Apparent_Duplicates dataset, then the corresponding OFPBDS_Improve data is improved with the enhanced data. For example, if data is missing in the OFPBDS, and present from the Target barriers, the attributes in the Target Barriers are integrated to the OFPBDS. In addition, if data has been updated, such as the fish passage status (fpbFPasSta) from a previous assessment, the more current attribute data is utilized. ESRI ArcInfo 9.3.1 2009 - 2011 Oregon Department of Fish and Wildlife Jon Bowers GIS Coordinator mailing and physical address
3406 Cherry Avenue NE
Salem Oregon 97303 United States 503-947-6097 jon.k.bowers@state.or.us Reconciled barrier features in the Oregon Fish Passage Barrier Data Standard (OFPBDS) with project information from the Oregon Watershed Restoration Inventory (OWRI) maintained by the Oregon Watershed Enhancement Board (OWEB). OWRI Reconciliation Process Use the most recent OWRI data. This geodatabase contains two feature classes: the full OWRI database and a subset feature class, fish_passage_projects, consisting of only the fish passage barrier improvement projects. The fish_passage_projects feature class constitutes records where the Project Type field = “fish passage” or “combined”; the Treatment field describes fish passage barrier modifications, replacement or removal, and Comment or Description fields mention fish passage, culverts, bridges, and/or dams. 1. Add the fish_passage_projects feature class to your MXD along with the OFPBDS version you are editing. 2. Do a Select by Location using the fish_passage_projects features and the OFPBDS features, within a distance of 150 meters. The selected OWRI points are now used for manual reconciliation. 3. Use the treatment field or TreatmentLUID field to divide the projects into three categories: Removed barriers, replaced barriers and modified barriers. Information regarding the projects is also available in the description and comment fields, and should be consulted if there is a question about what happened where. There may be cases where a barrier in your original data is the replaced or modified culvert that is recorded in the OWRI. 1. First, consider the date of the original data [fpbLocDt and fpbStaEvDt] in comparison to OWRI project dates [CompleteYear and CompleteMonth]. 2. Second, check the Fish Passage Status [fpbFPasSta]. A “Completely Passable” status in the original data would point toward a newer, possibly replaced or modified structure. 3. If it is determined that the original barrier feature and the OWRI feature are the same, only the fpbOrYr (if null) or fpbModDt (if applicable) fields would be populated from the OWRI record. Removed Barriers If the barrier was removed and not replaced, fill in the fpbRmvDt field in the OFPBDS data with the CompleteYear and CompleteMonth fields from OWRI. Following OFPBDS Business Rules: Data originators should populate these date elements as completely as possible. However, partial date information will be accepted. If the month and year are known, use zeros to populate the day portion of the date element. If only the year is known, use zeros to populate the month and day portion of the date element. If the date is unknown, use zeros to populate the entire element (e.g. 20011200, 20010000, 00000000). Replaced Barriers If the barrier was replaced with a new culvert, bridge, etc. there are two steps: Original OFPBDS feature is updated with the removed date, fpbRmvDt. A new feature is created for the new culvert, bridge, etc. and attribute data is copied and changed. 1. Select and Copy the original OFPBDS feature, and then Paste (Add) it to the appropriate feature class. You now have duplicate features. 2. Update the original record’s fpbRmvDt field: fpbRmvDt = CompleteYear and CompleteMonth fields per OWRI, following OFPBDS Business Rules, i.e., “20071000”. 3. Change attribute data for the new (copied) feature: a. fpbOFtrID and fpbOSiteID new features use the Site ID number (if available) or the OWEB Project Number if there is no SiteID number. If there is more than one feature for a Project, add a suffix, i.e., -A, -B for multiple features. b. fpbONm = “OWEB” c. fpbFPasSta = “Passable” d. fpbStaEvDt = CompleteYear and CompleteMonth fields per OWRI, following OFPBDS Business Rules. e. fpbStaEvMd = ”ByDesign” f. fpbOrYr = CompleteYear field per OWRI g. fpbFtrTy or fpbFtrNm if relevant, i.e. culvert replaced with bridge. h. Delete (make null) or update old information, copied from the original record, that is not related to the new feature, i.e. culvert subtype, height, length, width, slope, drop, and any other pertinent fields. i. Note: If you copied an OFPBDS feature that already has a fpbFtrID and fpbSiteID, these will need to be deleted (made null) and the Data Steward will assign new IDs. Modified Barriers If the barrier was modified, retrofitted, or improved in some manner, several fields in the OFPBDS records will be updated and the fields fpbModTy and/or fpbModDesc, in the version1_fields Table will be completed. 1. fpbModDt = CompleteYear and CompleteMonth field information from OWRI, following Business Rules for Dates. 2. fpbFPasSta = “Passable” Note: many modifications may only moderately improve passage; i.e., an upgrade from Blocked to Partial; so check OWRI comment fields or consider biologist verification if there is a question. 3. fpbStaEvDt = CompleteYear and CompleteMonth fields per OWRI, following Business Rules. 4. fpbStaEvMd = ”ByDesign” 5. fpbPasONm = “OWEB” 6. Populate the fbpModTy and/or fpbModDesc fields as appropriate: Baffles, StreamSim, Weirs, Other, Unknown. If “Other”, describe in the fpbModDes field. This might entail copying information from the OWRI comments or description fields. Issues with OWRI data - In cases where multiple passage barrier features were addressed as part of a single restoration project, especially where different types of features were addressed, it may be unclear which point represents which feature. - A large number of OWRI passage project locations have poor positional accuracy, in particular with records created with the StreamNet Event Mapper (~2005 or earlier). This issue hinders reconciliation with OFPBD, but it likely accounts for only a small percentage of the mismatches between OWRI and the current OFPBDS. OWRI records with a location confidence rating of “high” match up with OFPBD at the same rate (~15-20%) as those records with medium and low location confidence ratings. - All OWRI passage project records should be incorporated into OFPBD at a later date to maximize its comprehensiveness. There are numerous records in OWRI that are unlikely to be submitted to OFPBD by their ultimate originators because they fall on private industrial and private non-industrial forestlands. Incorporating OWRI records into OFPBD will update the database on passage problems already addressed. - Rules and assumptions for populating required attributes such as passage status (e.g. all OWRI passage projects now pass fish) will need to be developed when OWRI feature points are incorporated into the OFPBDS data. ESRI ArcInfo 9.3.1 2009 - 2011 GIS Coordinator 503-947-6097 jon.k.bowers@state.or.us Oregon Department of Fish and Wildlife Jon Bowers Converted Oregon Water Resources Department Dam Inventory data into the Oregon Fish Passage Barrier Data Standard (OFPBDS) format and loaded the data into the OFPBDS geodatabase. Metadata for OWRD dam data states the following: dams within the jurisdiction of Oregon Water Resource Department are defined by a dam height >= 10 feet and storage of >= 9.2 acre feet. OWRD dam data exist in an enterprise geodatabase as a point feature class, updated in June 2010, and a SQL database with ongoing updates. A geodatabase with a point feature class and an Excel Spreadsheet of 318 additional dams, were provided to the Data Steward in June and July 2010 respectively. A feature class was created for the Excel spreadsheet records by importing the spatial coordinates through ArcGIS. The two feature classes were checked for record duplication and then merged. A crosswalk between OWRD and OFPBDS attributes and attribute values was developed. Additionally, a methodology was developed to identify OWRD dam records that were not located in stream channels, i.e. waste water lagoons, and therefore not a fish passage barrier. OWRD staff was consulted for the crosswalk and the record selection methodology. Once the crosswalk was completed, OFPBDS fields were added to the database and attribute values for all the point features were populated in the OFPBDS fields. The data were exported in July 2010 into a replica copy of the enterprise geodatabase. Once the dam features were loaded in the OFPBDS replica, the data were analyzed for duplication. Where OWRD features were duplicates of OFPBDS (version 1) features, the OWRD dam feature replaced the OFPBDS (version 1) dam feature. Spatial proximity along with attribute similarity was used to identify potential - and likely - duplicates. The threshold distance default was 150 meters. However, upon visual inspection of the distance between OWRD and OFPBDS (version 1) dam features with matching attribute characteristics, some were over 2,000 feet apart. Potential duplicates, based on spatial proximity, were manually reviewed to identify those which were actual (confirmed) duplicates. Features which were potential duplicates due to proximity were compared by key attributes: Dam name, stream name, dam height, and owner. If there was still a question regarding duplication after this comparison, OWRD's water rights database was queried. Because OWRD does not collect information on fish passage status, where there was a definitive match between an OWRD dam record and an OFPBDS (version 1) dam feature with barrier status and fishway information, that attribute information was merged from the OFPBDS record to the OWRD record in order to retain it. ODFW is noted as the data source for those fields (fpbFPasONm). A second manual review based on feature name similarity further identified actual duplicates where feature points were greater than 150 meters apart. Dam features removed from the OFPBDS (version 1) database were ODFW records. Once the barrier features were compiled in the OFPBDS database and once features were analyzed for duplication, a limited effort was made to update dam features based upon the Oregon Watershed Enhancement Board's (OWEB) Oregon Watershed Restoration Inventory (OWRI). The point features and attributes were then loaded into the OFPBDS geodatabase. Specific notes regarding the OWRD dam data: * The coordinate system of the spatial coordinates in the fpbLong and fpbLat fields is GCS_North_American_1983. *The passage status for many of the dams is unknown at this time. Consequently, some of these barriers may be completely passable to most if not all the species and life stages that have a need to migrate through the affected stream reach. *Because OWRD does not collect information on fish passage status, where there was a definitive match between an OWRD dam record and an OFPBDS (version 1) dam feature with barrier status and fishway information, that attribute information was merged from the OFPBDS record to the OWRD record in order to retain it. ODFW is noted as the data source for those fields (fpbFPasONm). *Values for stream name (fpbStrNm) were provided by OWRD and are generally the storage water source as stated on the OWRD permit, not the location of the dam relative to a stream channel. * Where there is stream identifier (fpbStrID), and/or stream measure (fpbStrMeas) data are linear-referenced to the 1:24,000-scale PNW Framework Hydrography. 2010 ESRI ArcInfo 9.3.1 Oregon Department of Fish and Wildlife Jon Bowers GIS Coordinator 503-947-6097 jon.k.bowers@state.or.us 7:30-4 Converted Oregon Department of Forestry - Oregon Department of Fish and Wildlife (ODF-ODFW) Fish Presence barrier data into the Oregon Fish Passage Barrier Data Standard (OFPBDS) format and loaded the data into the OFPBDS geodatabase. ODF-ODFW Fish Presence barrier data consists of two data sets: attributed line features in an ODF Fish Presence geodatabase, last updated in June, 2010, and an Access database of culvert specifics, with location coordinates, taken from ODF-ODFW Fish Presence survey forms, compiled in 2000-2001 by the Oregon Department of Fish and Wildlife. A process for deriving barrier feature points from the ODF line features and a conversion outline, or crosswalk, between the Fish Presence line data, Fish Presence culvert database, and OFPBDS attributes and attribute values was developed. ODF and ODFW staff who compiled the Fish Presence data was consulted regarding the crosswalk. OFPBDS fields were then added to the ODF-ODFW Fish Presence barrier feature tables and attribute values were populated in the OFPBDS fields. ODF-ODFW Fish Presence barrier data was then analyzed for duplication between the two data sets and with OFPBDS records. Where ODF Fish Presence line feature derived barrier records were duplicates of Fish Presence culvert survey features, the line feature derived barrier was deleted. Where ODF-ODFW Fish Presence barrier features were duplicates of OFPBDS features, the ODF-ODFW Fish Presence barrier features were not added to the OFPBDS geodatabase. Where there was a definitive match between features, absent attribute information was migrated from the ODF-ODFW record to the OFPBDS feature in order to retain it. ODF-ODFW is noted as the data source for those fields. Spatial proximity along with attribute similarity was used to identify potential - and likely - duplicates. The threshold distance default was 150 meters. Points greater than 150 meters from a current OFPBDS feature location were considered new features and added. Features within 150 meters of OFPBDS features were considered potential duplicates, based on spatial proximity. Features which were potential duplicates due to proximity were compared by key attributes: stream name, road name, culvert type, width and length. If there was still a question regarding duplication after this comparison, the feature was put aside in a separate feature class for consultation. ODF-ODFW Fish Presence barrier features were also analyzed for duplication with the Oregon Watershed Enhancement Board's (OWEB) Oregon Watershed Restoration Inventory (OWRI). Where a match could be made between an OWRI record and an ODF-ODFW Fish Presence barrier feature, updates were made to pertinent fields. In October 2010, the ODF-ODFW Fish Presence barrier data were loaded into the OFPBDS enterprise geodatabase. Specific notes regarding the ODF-ODFW Fish Presence barrier feature data: * The coordinate system of the spatial coordinates in the fpbLong and fpbLat fields is GCS_North_American_1983. * The ODF Fish Presence feature class is attributed line features for watercourses within the state. The table contains a Barrier field to identify stream segments impacted by the presence of a fish barrier. To derive point features, ODFW selected records with a Barrier field value other than null or "None." Points were generated from the selected record lines [Barrier field value other than null or none] with the Feature Vertices to Points script/toolbox for line segments. Line segments above a barrier feature all carry the same barrier attribute; therefore upstream vertices need to be discarded. Arc direction varied in the feature class, so vertices (points) were checked manually against Fish Presence line work to identify the downstream terminus or point between stream segments with a barrier value other than null or none and segments with a none or null value. Line attributes transferred to the point. * ODF-ODFW Fish Presence survey data sources are varied, but are primarily Oregon Department of Forestry, Oregon Department of Fish and Wildlife, Federal land management agencies, private forest land owners, and private forestry consultants. Fish passage status evaluations are based on the ODF/ODFW Fish Presence Survey protocol described in Surveying Forest Streams for Fish Use. *Passage status for some barriers is unknown at this time. Consequently, some of these barriers may be completely passable to most if not all the species and life stages that have a need to migrate through the affected stream reach. * ODF Fish Presence data exists on hydrographic line work from several sources, including manually digitized watercourses. Where there is a stream identifier (fpbStrID), and/or stream measure (fpbStrMeas) data are linear-referenced to the 1:24,000-scale PNW Framework Hydrography. ODF Fish Presence data is available online: http://www.oregon.gov/ODF/GIS/fishpresence.shtml ESRI ArcInfo 9.3.1 2010 Oregon Department of Fish and Wildlife Jon Bowers GIS Coordinator 503-947-6097 jon.k.bowers@state.or.us Converted Oregon Department of Fish and Wildlife Aquatic Inventories Project (AIP) Habitat Unit data into the Oregon Fish Passage Barrier Data Standard (OFPBDS) format and loaded the data into the OFPBDS geodatabase. The ODFW Aquatic Inventories Project Habitat Unit data exists in ArcInfo Coverages packaged as Arc interchange files (.e00), last updated in 2010. Downloaded interchange files were imported into coverages in ArcCatalog, and then converted to geodatabase feature classes. A process for deriving barrier feature points from the AIP Habitat Unit line features and a crosswalk between the AIP Habitat Unit line data and OFPBDS attributes and attribute values was developed. ODFW staff, who compile the AIP Habitat Unit data, was consulted regarding deriving features and the crosswalk. OFPBDS fields were then added to the AIP Habitat Unit barrier feature tables and attribute values were populated in the OFPBDS fields. AIP Habitat Unit barrier data was then analyzed for duplication with OFPBDS records. Where AIP Habitat Unit line feature derived barrier records were duplicates of OFPBDS features, the AIP Habitat Unit barrier features were not added to the OFPBDS geodatabase. Where there was a definitive match between features, absent attribute information was migrated from the AIP Habitat Unit record to the OFPBDS feature in order to retain it. ODFW is noted as the data source for those fields. Spatial proximity along with attribute similarity was used to identify potential - and likely - duplicates. The threshold distance default was 150 meters. Points greater than 150 meters from a current OFPBDS feature location were considered new features and added. Features within 150 meters of OFPBDS features were considered potential duplicates, based on spatial proximity. Features which were potential duplicates due to proximity were compared by key attributes: feature type, stream name, road name, height, width and length. AIP Habitat Unit barrier features were also analyzed for duplication with the Oregon Watershed Enhancement Board's (OWEB) Oregon Watershed Restoration Inventory (OWRI). Where a match could be made between an OWRI record and an AIP Habitat Unit barrier feature, updates were made to pertinent fields. In February 2011, the AIP Habitat Unit barrier data were loaded into the OFPBDS enterprise geodatabase. Specific notes regarding the AIP Habitat Unit barrier feature data: * The coordinate system of the spatial coordinates in the fpbLong and fpbLat fields is GCS_North_American_1983. * The AIP Habitat Unit feature class is attributed line features for surveyed watercourses within the state. The geodatabase table contains a Unit Type field that identifies culvert crossings, artificial step structures and natural bedrock step features, i.e. waterfalls, along with a unique identifier field (HABUNT). To derive point barrier features, ODFW selected records with a Unit Type field value equal to these unit types [culvert crossings, steps created by structures, natural bedrock steps greater than 2 meters]. The Comment Code and Note fields also identified features such as dams, fish ladders and road fords. Points were generated from the selected record lines with the Feature Vertices to Points script/toolbox for line segments, using the start point of the line. Line attributes transferred to the point. *Fish passage status evaluations are based on coarse passage criteria relative to the feature type. For culverts, a drop or perch height over 0.5 feet = Partial; if the drop is equal to or greater than one foot, then a two foot or greater unit depth is needed immediately downstream (jump pool). If the downstream unit depth is equal to or greater than two feet, then the Fish Passage Status remains as "Partial". If the downstream unit depth is less than two feet, the Fish Passage Status = Blocked. If the slope of a culvert > 5% = Partial; if the drop > 3.2 feet = Blocked . For dams and other artificial step structures - if the Height > 0.5 foot = Partial; Height > 6.6 feet = Blocked; If the height is equal to or greater than one foot, then a two foot or greater unit depth is needed immediately downstream (jump pool). If the downstream unit depth is equal to or greater than two feet, then the Fish Passage Status remains as "Partial". If the downstream unit depth is less than two feet, the Fish Passage Status = Blocked. For natural features if the height is over 16 feet = Blocked. If the height is less than 16 feet = Unknown; if the slope is greater than or equal to 16 % over a distance of 200 meters = Blocked. Passage status for some barriers is unknown at this time. Consequently, some of these barriers may be completely passable to most if not all the species and life stages that have a need to migrate through the affected stream reach. * Project survey dates range from 1990 to 2009. Where data was seasonal, winter data was not used. * AIP Habitat Unit data exists on hydrographic line work generally at a scale of 1:100,000. Where there is a stream identifier (fpbStrID), and/or stream measure (fpbStrMeas) data are linear-referenced to the 1:24,000-scale PNW Framework Hydrography. AIP Habitat Unit data is available online: http://oregonstate.edu/dept/ODFW/freshwater/inventory/habitgis.html ESRI ArcInfo 9.3.1 2010 - 2011 GIS Coordinator 503-947-6097 jon.k.bowers@state.or.us 7:30 - 4 Oregon Department of Fish and Wildlife Jon Bowers Converted from the Umpqua Basin Fish Access Team (UBFAT) fish passage data into the Oregon fish Passage Barrier Data Standard (OFPBDS). Geospatial and tabular data was provided by UBFAT, as well as a document entitled "Umpqua Basin Fish Access Team (UBFAT) Basin Plan." The overall process for incorporating the UBFAT data into the fish passage barrier data standard was as follows: 1. Obtain UBFAT data. 2. Develop a crosswalk between UBFAT and OFPBDS, and develop a methodology to determine which records, if not all, to include in the standard. 3. Address any issues (like unique identifiers). 4. Convert data into the standard. 5. Provide standardized data back to UBFAT (and often also provide Steward-modified intermediate data developed during standardization, especially where identifiers were manipulated). 6. Throughout the entire process, UBFAT were consulted. The Steward worked with the UBFAT data "as is". In other words, the Steward did not attempt to review, edit or 'correct' UBFAT records, locations or attributes. The goal was to get as much information into the standard as possible. Most UBFAT barrier data contain attributes which match those in the standard as well as attributes which do not exist in the standard. Throughout the process of converting UBFAT data into the OFPBDS, a series of determinations, assumptions and decisions were made. A UBFAT - OFPBDS Crosswalk (spreadsheet) was developed and contains a record of this, along with a document detailing key GIS steps in the conversion process. A duplication process was performed as the final stage of analysis and documented within the UBFAT crosswalk to determine what, if any UBFAT barriers were duplicates of pre-existing OFPBDS barriers. Using a duplication analysis model to identify potential duplicates within 150 meters, 838 of the 2242 barriers were classified as potential duplicates. Out of the 838 potential duplicates, 650 were apparent duplicates, while the remaining 188 were questionable. The 650 apparent duplicate barriers were then used to update or improve missing or erroneous data in the corresponding OFPBDS features. The entire integration process using UBFAT's fish passage barrier information resulted in 369 bridges, 1,211 culverts, 1 dams, and 11 waterfalls. The total of fish passage barrier features imported to the OFPBDS from UBFAT is 1,592 features. ESRI ArcInfo 9.3.1 2010 Oregon Department of Fish and Wildlife Jon Bowers GIS Coordinator 503-947-6097 jon.k.bowers@state.or.us Converted Rogue Basin Fish Access Team (RBFAT) data into the Oregon Fish Passage Barrier Data Standard (OFPBDS) format and loaded the data into the OFPBDS geodatabase. The RBFAT data exists in an Excel spreadsheet and an Access database, last updated in 2005. Spatial coordinates for RBFAT barrier features were not available, with the exception of the Bear Creek Watershed. RBFAT data for the Bear Creek Watershed exists in a point feature class shapefile. RBFAT features with no spatial coordinates were manually located on DRGs or imagery and digitized, referring to legal coordinates, river miles, and ownership in the spreadsheet and database, and Oregon Water Resources Point of Diversion database and Decree map information. A conversion outline, or crosswalk, between RBFAT and OFPBDS attributes and attribute values was developed. RBFAT members who compiled the data were consulted regarding the crosswalk. OFPBDS fields were added to the Bear Creek Watershed geodatabase and attribute values were populated in the OFPBDS fields. Bear Creek Watershed records were then loaded into the RBFAT geodatabase. The RBFAT geodatabase and RBFAT Access tables were joined on the BarrierID field and attribute values were populated in the OFPBDS fields. RBFAT data was then analyzed for duplication with OFPBDS records. Where RBFAT features were duplicates of OFPBDS features, the RBFAT features were not added to the OFPBDS geodatabase. Spatial proximity along with attribute similarity was used to identify potential - and likely - duplicates. The threshold distance default was 150 meters. Points greater than 150 meters from a current OFPBDS feature location were considered new features and added. Features within 150 meters of OFPBDS features were considered potential duplicates, based on spatial proximity. Features which were potential duplicates due to proximity were compared by key attributes: stream name, road name, culvert type, width and length. If there was still a question regarding duplication after this comparison, the feature was put aside in a separate feature class for consultation. Where there was a definitive match between a RBFAT feature and an OFPBDS feature, missing attribute information was merged from the RBFAT record to the OFPBDS record in order to retain it. RBFAT is noted as the data source for those fields. RBFAT barrier features were also analyzed for duplication with the Oregon Watershed Enhancement Board's (OWEB) Oregon Watershed Restoration Inventory (OWRI). Where a match could be made between an OWRI record and a RBFAT feature, updates were made to pertinent fields. The RBFAT data were exported in October 2010 into a replica copy of the enterprise geodatabase and posted to the OFPBDS enterprise geodatabase. Specific notes regarding the RBFAT data: * The coordinate system of the spatial coordinates in the fpbLong and fpbLat fields is GCS_North_American_1983. * Where there is stream identifier (fpbStrID), and/or stream measure (fpbStrMeas) data are linear-referenced to the 1:24,000-scale PNW Framework Hydrography. RBFAT fish passage barrier data is available online: http://www.restoretherogue.org/docs/rbfat_barrier_prioritization92703.xls 2010 ESRI ArcInfo 9.3.1 Oregon Department of Fish and Wildlife Jon Bowers GIS Coordinator 503-947-6097 jon.k.bowers@state.or.us Converted Benton County's fish passage data into the Oregon fish Passage Barrier Data Standard (OFPBDS). Geospatial and tabular data was provided by BENTON COUNTY, as well as a document entitled "A comprehensive Assessment of Fish Passage Barriers in the Scappoose Bay Watershed." The overall process for incorporating Benton County's data into the fish passage barrier data standard was as follows: 1. Obtain Benton County data. 2. Develop a crosswalk between Benton County and OFPBDS, and develop a methodology to determine which records, if not all, to include in the standard. 3. Address any issues (like unique identifiers). 4. Convert data into the standard. 5. Provide standardized data back to Benton County (and often also provide Steward-modified intermediate data developed during standardization, especially where identifiers were manipulated). 6. Throughout the entire process, Benton County was consulted. The Steward worked with the Benton County data "as is". In other words, the Steward did not attempt to review, edit or 'correct' Benton County records, locations or attributes. The goal was to get as much information into the standard as possible. Most Benton County barrier data contain attributes which match those in the standard as well as attributes which do not exist in the standard. Throughout the process of converting Benton County data into the OFPBDS, a series of determinations, assumptions and decisions were made. A Benton County - OFPBDS Crosswalk (spreadsheet) was developed and contains a record of this, along with a document detailing key GIS steps in the conversion process. A duplication process was performed as the final stage of analysis and documented within the Benton County crosswalk to determine what, if any Benton County barriers were duplicates of pre-existing OFPBDS barriers. Using a duplication analysis model to identify potential duplicates within 150 meters, 93 of the 571 barriers were classified as potential duplicates. Out of the 93 potential duplicates, 60 were apparent duplicates, while the remaining 33 were questionable. The 60 apparent duplicate barriers were then used to update or improve missing or erroneous data in the corresponding OFPBDS features. The entire integration process using Benton County's fish passage barrier information resulted in 224 bridges, 2 cascades, 219 culverts, 5 dams, 4 waterfalls, 2 fords, 1 weir, 4 other known fish passage barrier feature including debris jams, and 13 unknown features. The total of fish passage barrier features imported to the OFPBDS from Benton County is 474 features. ESRI ArcInfo 9.3.1 2010 Converted Wallowa County BPA/Nez Perce fish barrier inventory data into the Oregon Fish Passage Barrier Data Standard (OFPBDS) format and loaded the data into the OFPBDS geodatabase. Wallowa County BPA/Nez Perce fish barrier data exists in an Excel spreadsheet, last updated in 2007. A conversion outline, or crosswalk, between Wallowa County BPA/Nez Perce and OFPBDS attributes and attribute values was developed. Wallowa County BPA/Nez Perce staff who compiled the data was consulted regarding the crosswalk. OFPBDS fields were then added to the Wallowa County BPA/Nez Perce fish barrier database and attribute values for all the point features were populated in the OFPBDS fields. The Wallowa County BPA/Nez Perce fish barrier data was then analyzed for duplication with the OFPBDS (version 1) records. Where Wallowa County BPA/Nez Perce fish barrier features were duplicates of OFPBDS (version 1) features, the Wallowa County BPA/Nez Perce fish barrier feature replaced the OFPBDS (version 1) feature. Spatial proximity along with attribute similarity was used to identify potential - and likely - duplicates. The threshold distance default was 150 meters. Points greater than 150 meters from a current OFPBDS (version 1) feature location were considered new features and added. Features within 150 meters of OFPBDS (version 1) features were considered potential duplicates, based on spatial proximity. Features which were potential duplicates due to proximity were compared by key attributes: stream name, road name, feature type and subtype. Wallowa County BPA/Nez Perce fish barrier features were also analyzed for duplication with the Oregon Watershed Enhancement Board's (OWEB) Oregon Watershed Restoration Inventory (OWRI). Where a match could be made between an OWRI record and a Wallowa County BPA/Nez Perce fish barrier feature, updates were made to pertinent fields. The Wallowa County BPA/Nez Perce fish barrier data were exported in September 2010 into a replica copy of the enterprise geodatabase and posted to the OFPBDS enterprise geodatabase. Specific notes regarding the Wallowa County BPA/Nez Perce fish barrier data: * The coordinate system of the spatial coordinates in the fpbLong and fpbLat fields is GCS_North_American_1983. *The Wallowa County BPA/Nez Perce fish barrier inventory used a U.S. Forest Service/BLM Full Assessment protocol, which includes both barrier and hydraulic analysis, to evaluate fish passage status. This protocol may result in a high number of passage status evaluations = blocked. For information on the protocol, refer to Explanations and Instructions for Passage Through Road/Stream Crossings Inventory Form (Jacobson 2003) and Region 1 Fish Passage Evaluation Criteria (Jacobson 2003). * Where there is stream identifier (fpbStrID), and/or stream measure (fpbStrMeas) data are linear-referenced to the 1:24,000-scale PNW Framework Hydrography. Wallowa County BPA/Nez Perce fish barrier features information is available online at BPA Streamnet Data Store (BPA Project No. 2002-073-00). Oregon Department of Fish and Wildlife Jon Bowers GIS Coordinator 503-947-6097 jon.k.bowers@state.or.us ESRI ArcInfo 9.3.1 2010 Oregon Department of Fish and Wildlife Jon Bowers GIS Coordinator 503-947-6097 jon.k.bowers@state.or.us Converted Washington County fish passage assessment culvert data into the Oregon Fish Passage Barrier Data Standard (OFPBDS) format and loaded the data into the OFPBDS geodatabase. The Washington County culvert data exists in an Excel spreadsheet, last updated in 2006 for the Dairy Creek watershed and in 2008 for the Gales Creek Watershed. A conversion outline, or crosswalk, between Washington County and OFPBDS attributes and attribute values was developed. Washington County staff who compiled the data was consulted regarding the crosswalk. OFPBDS fields were then added to the Washington County records and attribute values for all barrier features were populated in the OFPBDS fields. Washington County data was then analyzed for duplication with the OFPBDS records. Where Washington County fish barrier features were duplicates of OFPBDS features, the Washington County fish barrier feature replaced the OFPBDS feature. Spatial proximity along with attribute similarity was used to identify potential - and likely - duplicates. The threshold distance default was 150 meters. Points greater than 150 meters from a current OFPBDS feature location were considered new features and added. Features within 150 meters of OFPBDS (version 1) features were considered potential duplicates, based on spatial proximity. Features which were potential duplicates due to proximity were compared by key attributes: stream name, road name, culvert type, width and length. If there was still a question regarding duplication after this comparison, the feature was put aside in a separate feature class for consultation. Washington County barrier features were also analyzed for duplication with the Oregon Watershed Enhancement Board's (OWEB) Oregon Watershed Restoration Inventory (OWRI). Where a match could be made between an OWRI record and a Washington County feature, updates were made to pertinent fields. The Washington County data were exported in October 2010 into a replica copy of the enterprise geodatabase and posted to the OFPBDS enterprise geodatabase. Specific notes regarding the Washington County fish passage culvert data: * The coordinate system of the spatial coordinates in the fpbLong and fpbLat fields is GCS_North_American_1983. * Culverts smaller than 15 inches in diameter were excluded from the Washington County fish passage assessment as were culverts carrying streams with gradients over 15%. * The culvert survey measured four surrogate indicators to determine a culvert's ability to pass fish: culvert gradient, stream bankfull width, inlet blockage, and outlet perch. The survey method selected was based on the BLM's Fish Passage Through Road Crossing Assessment. Barrier severity determination was based on the BLM Coarse Screen Filter Version 2.2 The filter identifies a culvert's barrier level based on the requirements of juvenile salmonids. *Passage status for a number of culverts was undetermined at the time data were integrated. These culverts require additional analysis that Washington County intends to undertake, to determine their fish passage status. Consequently, these barriers may completely or partially pass most if not all the species and life stages that have a need to migrate through the affected stream reach. * Where there is stream identifier (fpbStrID), and/or stream measure (fpbStrMeas) data are linear-referenced to the 1:24,000-scale PNW Framework Hydrography. The Diary Creek Watershed Study is available online: http://www.co.washington.or.us/LUT/Divisions/Operations/upload/fishpr07.pdf ESRI ArcInfo 9.3.1 2010 Oregon Department of Fish and Wildlife Jon Bowers GIS Coordinator 503-947-6097 jon.k.bowers@state.or.us Data was converted from the Clackamas River Basin Council (CRBC) fish passage data into the Oregon fish Passage Barrier Data Standard (OFPBDS). Geospatial and tabular data was provided by CRBC, as well as two documents entitled "Clear and Foster Creek Fish Passage Assessment and Prioritization Project," and "Deep, Goose and Eagle Creeks Fish Passage Assessment." The overall process for incorporating the CRBC data into the fish passage barrier data standard was as follows: 1. Obtain CRBC data. 2. Develop a crosswalk between CRBC and OFPBDS, and develop a methodology to determine which records, if not all, to include in the standard. 3. Address any issues (like unique identifiers). 4. Convert data into the standard. 5. Provide standardized data back to CRBC (and often also provide Steward-modified intermediate data developed during standardization, especially where identifiers were manipulated). 6. Throughout the entire process, CRBC was consulted. The Steward worked with the CRBC data "as is". In other words, the Steward did not attempt to review, edit or 'correct' CRBC records, locations or attributes. The goal was to get as much information into the standard as possible. Most CRBC barrier data contain attributes which match those in the standard as well as attributes which do not exist in the standard. Throughout the process of converting CRBC data into the OFPBDS, a series of determinations, assumptions and decisions were made. A CRBC - OFPBDS Crosswalk (spreadsheet) was developed and contains a record of this, along with a document detailing key GIS steps in the conversion process. A duplication process was performed as the final stage of analysis and documented within the CRBC crosswalk to determine what, if any CRBC barriers were duplicates of pre-existing OFPBDS barriers. Using a duplication analysis model to identify potential duplicates within 150 meters, 90 of the 558 barriers were classified as potential duplicates. Out of the 90 potential duplicates, 48 were apparent duplicates, while the remaining 46 were questionable. The 48 apparent duplicate barriers were then used to update or improve missing or erroneous data in the corresponding OFPBDS features. The entire integration process using CRBC's fish passage barrier information resulted in the addition of 469 culverts. ESRI ArcInfo 9.3.1 2010 Data was converted from the Calapooia Watershed Council (CWC) fish passage data into the Oregon fish Passage Barrier Data Standard (OFPBDS). Geospatial and tabular data was provided by CWC, as well as a document entitled "Calapooia Watershed Fish Passage Assessment." The overall process for incorporating the CWC data into the fish passage barrier data standard was as follows: 1. Obtain CWC data. 2. Develop a crosswalk between CWC and OFPBDS, and develop a methodology to determine which records, if not all, to include in the standard. 3. Address any issues (like unique identifiers). 4. Convert data into the standard. 5. Provide standardized data back to CWC (and often also provide Steward-modified intermediate data developed during standardization, especially where identifiers were manipulated). 6. Throughout the entire process, CWC was consulted. The Steward worked with the CWC data "as is". In other words, the Steward did not attempt to review, edit or 'correct' CWC records, locations or attributes. The goal was to get as much information into the standard as possible. Most CWC barrier data contain attributes which match those in the standard as well as attributes which do not exist in the standard. Throughout the process of converting CWC data into the OFPBDS, a series of determinations, assumptions and decisions were made. A CWC - OFPBDS Crosswalk (spreadsheet) was developed and contains a record of this, along with a document detailing key GIS steps in the conversion process. A duplication process was performed as the final stage of analysis and documented within the CWC crosswalk to determine what, if any CWC barriers were duplicates of pre-existing OFPBDS barriers. Using a duplication analysis model to identify potential duplicates within 150 meters, 65 of the 116 barriers were classified as potential duplicates. Out of the 65 potential duplicates, 48 were apparent duplicates, while the remaining 17 were questionable. The 48 apparent duplicate barriers were then used to update or improve missing or erroneous data in the corresponding OFPBDS features. The entire integration process using CWC's fish passage barrier information resulted in the addition of 68 culverts. GIS Coordinator 503-947-6097 jon.k.bowers@state.or.us Oregon Department of Fish and Wildlife Jon Bowers ESRI ArcInfo 9.3.1 2010 Oregon Department of Fish and Wildlife Jon Bowers GIS Coordinator 503-947-6097 jon.k.bowers@state.or.us Data was integrated from the Santiam Watershed Council's (Santiam WC) fish passage data into the Oregon fish Passage Barrier Data Standard (OFPBDS). Geospatial and tabular data was provided by Santiam WC. The overall process for incorporating the Santiam data into the fish passage barrier data standard was as follows: 1. Obtain Santiam WC data (107 records). 2. A crosswalk was not necessary for Santiam WC because they used ODFW's schema and existing barriers. 3. Santiam WC updated and corrected attributes of these existing fish passage barriers, most importantly, barrier dimensions and fish passage status. 4. Where Santiam WC identified multiple features at a single location, fish passage barriers records were added. Exactly 18 barriers were added, and assigned Santiam WC as the fish passage barrier originator (fpbOrNm). The remaining features retained ODFW as their original source. 5. Provide standardized data back to Santiam WC (and often also provide Steward-modified intermediate data developed during standardization, especially where identifiers were manipulated). 6. Throughout the entire process, Santiam WC was consulted. The Steward worked with the Santiam WC data "as is". In other words, the Steward did not attempt to review, edit or 'correct' Santiam WC records, locations or attributes. The goal was to get as much information into the standard as possible. Most Santiam WC barrier data contain attributes which match those in the standard as well as attributes which do not exist in the standard. The entire integration process using Santiam WC's fish passage barrier information resulted in the addition of 18 culverts. ESRI ArcInfo 9.3.1 2010 Oregon Department of Fish and Wildlife Jon Bowers GIS Coordinator 503-947-6097 jon.k.bowers@state.or.us Converted the Scappoose Bay Watershed Council's (SBWC) fish passage data into the Oregon fish Passage Barrier Data Standard (OFPBDS). Geospatial and tabular data was provided by SBWC, as well as a document entitled "A comprehensive Assessment of Fish Passage Barriers in the Scappoose Bay Watershed." The overall process for incorporating SBWC data into the fish passage barrier data standard was as follows: 1. Obtain SBWC data. 2. Develop a crosswalk between SBWC and OFPBDS, and develop a methodology to determine which records, if not all, to include in the standard. 3. Address any issues (like unique identifiers). 4. Convert data into the standard. 5. Provide standardized data back to SBWC (and often also provide Steward-modified intermediate data developed during standardization, especially where identifiers were manipulated). 6. Throughout the entire process, SBWC were consulted. The Steward worked with the SBWC data "as is". In other words, the Steward did not attempt to review, edit or 'correct' SBWC records, locations or attributes. The goal was to get as much information into the standard as possible. Most SBWC barrier data contain attributes which match those in the standard as well as attributes which do not exist in the standard. Throughout the process of converting SBWC data into the OFPBDS, a series of determinations, assumptions and decisions were made. A SBWC - OFPBDS Crosswalk (spreadsheet) was developed and contains a record of this, along with a document detailing key GIS steps in the conversion process. A duplication process was performed as the final stage of analysis to determine what, if any SBWC barriers were duplicates of pre-existing OFPBDS barriers. It was determined using a 150 meter distance analysis that 13 barriers had in fact already existed in the OFPBDS dataset. In comparing the two, it was determined that the 13 newer SBWC contained more comprehensive and updated data, and subsequently, the 13 records were removed in the OFPBDS, and replaced by the SBWC records. The entire integration process using SBWC's fish passage barrier information resulted in 1 bridge, 96 culverts, 12 dams, and 1 tidegate. The total of fish passage barrier features imported to the OFPBDS from SBWC is 110 features. ESRI ArcInfo 9.3.1 2010 Oregon Department of Fish and Wildlife Jon Bowers GIS Coordinator 503-947-6097 jon.k.bowers@state.or.us Converted Siuslaw Watershed Council culvert inventory data into the Oregon Fish Passage Barrier Data Standard (OFPBDS) format and loaded the data into the OFPBDS geodatabase. Siuslaw Watershed Council culvert data exists in a point feature class shapefile, last updated in 2006. A conversion outline, or crosswalk, between Siuslaw Watershed Council and OFPBDS attributes and attribute values was developed. Siuslaw Watershed Council members who compiled the data were consulted regarding the crosswalk. U.S. Forest Service records in the Siuslaw Watershed Council data were excluded, pending receipt and review of statewide Forest Service data. OFPBDS fields were then added to the Siuslaw database and attribute values for all the point features were populated in the OFPBDS fields. The Siuslaw Watershed Council data was then analyzed for duplication with the OFPBDS (version 1) records. Duplicate features were not added to the OFPBDS. Spatial proximity along with attribute similarity was used to identify potential - and likely - duplicates. The threshold distance default was 150 meters. Points greater than 150 meters from a current OFPBDS (version 1) feature location were considered new features and added. Features within 150 meters of OFPBDS (version 1) features were considered potential duplicates, based on spatial proximity. Features which were potential duplicates due to proximity were compared by key attributes: stream name, road name, culvert type, width and length. If there was still a question regarding duplication after this comparison, the feature was put aside in a separate feature class for consultation. Where there was a definitive match between a Siuslaw Watershed Council feature and an OFPBDS (version 1) culvert feature, missing attribute information was merged from the Siuslaw Watershed Council record to the OFPBDS record in order to retain it. Siuslaw Watershed Council is noted as the data source for those fields. Siuslaw Watershed Council features were also analyzed for duplication with the Oregon Watershed Enhancement Board's (OWEB) Oregon Watershed Restoration Inventory (OWRI). Where a match could be made between an OWRI record and a Siuslaw Watershed Council feature, updates were made to pertinent fields. The Siuslaw Watershed Council data were exported in September 2010 into a replica copy of the enterprise geodatabase and posted to the OFPBDS enterprise geodatabase. Specific notes regarding the Siuslaw Watershed Council data: * The coordinate system of the spatial coordinates in the fpbLong and fpbLat fields is GCS_North_American_1983. *The passage status for many of the culverts is unknown at this time. Consequently, some of these barriers may be completely passable to most if not all the species and life stages that have a need to migrate through the affected stream reach. *The Siuslaw Watershed Council data includes features located by field surveys conducted for the Council, as well as records garnered from multiple agencies, including the U.S. Forest Service and Bureau of Land Management, the Oregon Department of Transportation and Watershed Enhancement Board, and Lane County. *Where there was a definitive match between an OFPBDS (version 1) and Siuslaw Watershed Council features, additional attribute information was merged from the Siuslaw Watershed Council record to the OFPBDS record in order to retain it. Siuslaw Watershed Council is noted as the data source for those fields. * Where there is stream identifier (fpbStrID), and/or stream measure (fpbStrMeas) data are linear-referenced to the 1:24,000-scale PNW Framework Hydrography. Siuslaw Watershed Council information is available online at http://www.siuslaw.org/ ESRI ArcInfo 9.3.1 2010 1996 2011 ODFW Fish Passage Barrier Data See process steps for more details. ODOT Drainage Facility Management System See process steps for more details. BLM - District Level Fish Passage Barrier Data See process steps for more details. Oregon Watershed Restoration Inventory See process steps for more details. Oregon Water Resources Department Dams Dataset See process steps for more details. Oregon Department of Forestry Fish Presence Survey Data See process steps for more details. Umpqua Basin Fish Access Team Fish Passage Barrier Data See process steps for more details. Rogue Basin Fish Access Team Fish Passage Barrier Data See process steps for more details. Benton County Soil and Water Conservation District Fish Passage Barrier Data See process steps for more details. Nez Perce - Wallowa County Fish Passage Barrier Data See process steps for more details. Washington County Fish Passage Barrier Data See process steps for more details. Clackamas Basin Council Fish Passage Barrier Data See process steps for more details. Calapooia Watershed Council Fish Passage Barrier Data See process steps for more details. Santiam Watershed Council Fish Passage Barrier Data See process steps for more details. Scappoose Bay Watershed Council Fish Passage Barrier Data See process steps for more details. Siuslaw Watershed Council See process steps for more details. Jon Bowers ODFW GIS Coordinator 503-947-6097 jon.k.bowers@state.or.us United States Forest Service (USFS) Culvert Inventory data were converted into the Oregon Fish Passage Barrier Data Standard (OFPBDS) format and loaded into the OFPBDS geodatabase. Data were obtained from the following National Forests: Deschutes, Fremont - Winema, Malheur, Mt. Hood, Ochoco, Rogue River - Siskiyou, Siuslaw, Umatilla, Umpqua, Wallowa Whitman, and Willamette. Point feature classes were provided from each of the forests giving culvert locations and a varying amount of attribute data. Additional attribute data from two regional datasets were used to augment the attributes furnished by the forests. A file geodatabase was constructed for each forest to contain the source spatial and tabular data and the derived data products. The number of records per forest varied from 40 to over 400, and the total number of records processed was 3,046. A crosswalk between USFS and OFPBDS attributes and attribute values was developed for each forest. The crosswalk consists of three sections: a section that contains summary information relating to the entire dataset; a section for “Required” attributes, which provide information considered essential to the usefulness of the data; and a section for “Optional” attributes, which provide supplementary information that provide additional details not found in the required attributes . An initial crosswalk was developed and sent to each forest presenting the mapping between USFS attributes and OFPBDS attributes and describing the processing necessary to transform the USFS data to meet OFPBDS standards. Each forest was invited to review the crosswalk and submit comments or concerns related to the proposed processing of their data. Processing the data from each forest took place in four primary phases executed sequentially. The objective of the processing was to identify and upload fish passage barriers in the forest data that were not yet represented in the OFPBDS dataset and to update existing records with more current information coming from the forests. The first phase of the processing established a correspondence between the USFS data and the OFPBDS data such that USFS attributes were transformed to meet the standards set forth in the Oregon Fish Passage Barrier Data Standard document. The resulting attribute values were loaded into empty “Required” and “Optional” fields corresponding to the OFPBDS attributes appended to each record in the USFS point feature class. The next phase of processing compared fish passage barrier point features in the USFS data to existing features in the OFPBDS dataset. Spatial proximity along with attribute similarity were used to identify potential and likely duplicates. A default threshold distance of 150 meters was used to partition the USFS points into those too distant from any OFPBDS point to be considered to represent the same feature and those close enough to be potential duplicates. Taking the potential duplicates, a script was run that compares the values of selected attributes and considers spatial proximity to calculate a measure of how much evidence exists in the data to indicate duplicate points. A summary table was constructed to permit quick comparisons of attribute pairs and see the cause of a mismatch. Where the evidence was low, a close manual examination of the pair of points in ArcGIS was conducted to confirm whether they represent the same or different features. Where the evidence for matched points was high, e.g. points less than 30 meters apart, a quick look was usually sufficient to confirm the match. In order to obtain additional information that might clarify the status of culverts that had been removed or replaced, a second proximity analysis was run against the Oregon Watershed Enhancement Board’s (OWEB) Oregon Watershed Restoration Inventory (OWRI). The same threshold of 150 meters was used, and OWRI points close to USFS points were manually examined to determine if any recent maintenance action may have affected the status of the culvert. The third phase of processing the data involved linearly referencing the new USFS points to be added to the OFPBDS dataset. Each new point was spatially analyzed to determine where it falls on a mapped stream. The Framework hydrography dataset was used to reference each barrier point, assign a unique stream identifier and stream distance measure. The final phase in the processing consisted of a quality check on the new data points prior to loading the data into the OFPBDS dataset. In the case of USFS barriers that were already represented in the OFPBDS data, a check was performed to determine if the USFS data contained new fish passage information. If so, the fish passage status (fpbFPasSta), fish passage data originator (fpbFPasONm), and revision date (fpbRevDt) were updated in the OFPBDS dataset. For new fish passage barrier records, the data were loaded into an editable version of the OFPBDS dataset, which was uploaded to a QA version and verified before being incorporated into the operational version. Specific notes regarding USFS fish passage barrier data: There was a wide variation in the quantity and quality of the initial datasets obtained from the forests. The number of attributes varied from less than 20 to well over 100. Approximately half of the datasets were well-attributed, while a few had most of the “Required” attributes and some of the “Optional”, and the remaining datasets did not have many of either category of attribute. To supplement the attributes supplied by the forests, the forests’ attribute tables were linked to available regional fish passage datasets, which supplied additional attributes. Two types of feature identifier schemes were employed in the USFS data. One scheme utilizes a long integer of 10 or more digits, which is unique across forests. The other scheme is basically a sequential numbering of the records from one to the total number of records. There were two ramifications of this situation. In order to connect datasets with the sequential numbering to regional data, additional attributes had to be used to achieve a unique match.. The second impact was that in order to have identifiers unique across forests, the originator feature ID (fpbOFtrID) was made to consist of a concatenation of the forest name and the identifier used within the forest. Physical data on culverts was often lacking. In many cases the basic parameters of height, width and length were absent. In other cases the values were suspect, either because they seemed to be in the wrong units or because they differed significantly from other measurements at the same location. In order to represent slopes as positive numbers, the sign had to be inverted. Drop values also were inverted to create positive numbers, but there were many instances of both positive and negative drops in the same dataset. The existence of multiple culverts, in space or over time, was usually not clearly represented. In a few instances multiple culverts were represented by multiple features in the dataset and identified as such. More commonly, the only indication of the existence of multiple features was a note in the “Comments” field. Similarly, the only indication of a culvert replacement or removal was often in the form of a cursory note, making it difficult to determine whether the data in the current record represented a culvert that had been taken out or one that replaced it. ArcInfo 10.0 8/2011 - 12/2011 US Forest Service See process step information for more details Barrier features in the Oregon Fish Passage Barrier Data Standard (OFPBDS) dataset contain the attributes which were provided by the data originators. When barrier data are converted into the OFPBDS format, attributes for certain fields (e.g. fish passage status - fpbFPasSta) become standardized. Among the source datasets, there is wide variation in the number and type of attributes, including those that relate to OFPBDS fields. Attribute values for particular fields are not always consistent among the originators. Many barrier records may contain information which does not reflect existing barrier conditions because feature conditions have changed since the last assessment or because more recent information has not yet been incorporated into the database. Many of the source datasets contain records collected years ago or records which are considered temporary (such as those ODOT features with a fpbOFtrID value beginning with "T"). Some features contain current and accurate attribution and others may not. In cases where attributes have been populated through automated data processing routines (e.g. linear referencing), quality assurance measures have been taken to identify and correct inaccurate assignement of attribute values. In order to improve the quality of the OFPBDS dataset over the coming months and years, field verification of fish passage barriers will be essential for improving the currency, completeness and accuracy of the data. The Oregon Fish Passage Barrier Data Standard (OFPBDS) database is not a comprehensive representation of fish passage barriers in Oregon. Version 2 contains barrier features from approximately 16 agencies / organizations that are listed in the abstract. The OFPBDS database may not contain all the barrier records from any one agency. Existing fish passage barrier data from most agencies / organizations in Oregon have been incorporated into the OFPBDS database. Data from the US Forest Service, Clackamas county and likely other sources will be incorporated into a future version of the dataset. Though the intent is to make the OFPBDS database comprehensive, current and accurate, the dataset remains a work in progress. Locational accuracy of barrier features varies. The fpbLocAccu attribute provides a measure for positional accuracy for a given record. Some of the barrier records are accurately mapped (within 40 feet), others are not (with features mapped beyond 40 feet of their true location, some possibly hundreds of feet away). Jon Bowers Oregon Dept. of Fish and Wildlife GIS Coordinator Jon Bowers 4034 Fairview Industrial Dr SE Salem Oregon 97302 jon.k.bowers@state.or.us 503-947-6097 Jon Bowers Jon Bowers Oregon Dept. of Fish and Wildlife GIS Coordinator Jon Bowers 4034 Fairview Industrial Dr SE Salem Oregon 97302 jon.k.bowers@state.or.us 503-947-6097 Jon Bowers ofpbds_pt The OFPBDS dataset represents a compilation of data from at least 19 separate state and federal agencies, tribes and non-profit organizations including watershed councils. Compiled fish passage barrier data from multiple agencies, counties, watershed councils and one tribe into the Oregon Fish Passage Barrier Data Standard (OFPBDS) geodatabase. In compiling fish passage barrier features from the different data originators into the OFPBDS database, the Data Steward followed some general guidelines: 1. Identify and acquire data and metadata. 2. Data Discovery. Review metadata to ensure an understanding of the data; its primary content, characteristics, capabilities and limitations. Develop key questions of usability for purposes of meeting the requirements of the standard, especially related to unique IDs, location, barrier type and passage status. 3. Consult with originator to answer questions and resolve outstanding issues (e.g. persistent unique IDs) for meeting the requirements of the standard. 4. Determine appropriate subset to incorporate, if any, based on presence of location data, unique IDs, specific attribution (e.g., exclude cross drain culverts - culverts not on stream crossings). 5. Develop a proposed methodology for converting the data into the OFPBDS format. Seek input and approval from the data originator for the data conversion methodology. Address issues as necessary so there is agreement on the methodology. 6. Process the data into the standard format. 7. Perform quality assurance routines to ensure that the data have been converted to the standardized format according to plan. 8. Analyze the data to determine whether there are duplicate barrier records coming from multiple sources. Address duplicate records according to established protocols that are found in the Barrier Data Management Plan. 9. Linear reference barrier features. 10. Reconcile barrier data with the Oregon Watershed Restoration Inventory. 11. Document data processing steps. 12. Load the data into the OFPBDS geodatabase. The steps outllined above were used by the Data Steward to standardize barrier data from the multiple sources that were compiled and integrated. The process by which data were converted into the OFPBDS format and loaded into the OFPBDS database required collaboration with the data originators and the development of numerous record selection methodologies, attribute crosswalks, decision trees, issue resolutions, and data management protocols. Common difficulties included ensuring that all records from a given originator had a unique originator feature identifier (fpbOFtrID) and determining how to crosswalk various criteria used for assessing fish passage status. If requested, more detailed metadata on the standardization of barrier data can be provided. Oregon Dept. of Transporation Oregon Watershed Enhancement Board (OWEB) - Oregon Watershed Restoration Inventory Reconciled barrier features in the Oregon Fish Passage Barrier Data Standard (OFPBDS) with project information from the Oregon Watershed Restoration Inventory (OWRI) maintained by the Oregon Watershed Enhancement Board (OWEB). OWRI Reconciliation Process Use the most recent OWRI data. This geodatabase contains two feature classes: the full OWRI database and a subset feature class, fish_passage_projects, consisting of only the fish passage barrier improvement projects. The fish_passage_projects feature class constitutes records where the Project Type field = “fish passage” or “combined”; the Treatment field describes fish passage barrier modifications, replacement or removal, and Comment or Description fields mention fish passage, culverts, bridges, and/or dams. 1. Add the fish_passage_projects feature class to your MXD along with the OFPBDS version you are editing. 2. Do a Select by Location using the fish_passage_projects features and the OFPBDS features, within a distance of 150 meters. The selected OWRI points are now used for manual reconciliation. 3. Use the treatment field or TreatmentLUID field to divide the projects into three categories: Removed barriers, replaced barriers and modified barriers. Information regarding the projects is also available in the description and comment fields, and should be consulted if there is a question about what happened where. There may be cases where a barrier in your original data is the replaced or modified culvert that is recorded in the OWRI. 1. First, consider the date of the original data [fpbLocDt and fpbStaEvDt] in comparison to OWRI project dates [CompleteYear and CompleteMonth]. 2. Second, check the Fish Passage Status [fpbFPasSta]. A “Completely Passable” status in the original data would point toward a newer, possibly replaced or modified structure. 3. If it is determined that the original barrier feature and the OWRI feature are the same, only the fpbOrYr (if null) or fpbModDt (if applicable) fields would be populated from the OWRI record. Removed Barriers If the barrier was removed and not replaced, fill in the fpbRmvDt field in the OFPBDS data with the CompleteYear and CompleteMonth fields from OWRI. Following OFPBDS Business Rules: Data originators should populate these date elements as completely as possible. However, partial date information will be accepted. If the month and year are known, use zeros to populate the day portion of the date element. If only the year is known, use zeros to populate the month and day portion of the date element. If the date is unknown, use zeros to populate the entire element (e.g. 20011200, 20010000, 00000000). Replaced Barriers If the barrier was replaced with a new culvert, bridge, etc. there are two steps: Original OFPBDS feature is updated with the removed date, fpbRmvDt. A new feature is created for the new culvert, bridge, etc. and attribute data is copied and changed. 1. Select and Copy the original OFPBDS feature, and then Paste (Add) it to the appropriate feature class. You now have duplicate features. 2. Update the original record’s fpbRmvDt field: fpbRmvDt = CompleteYear and CompleteMonth fields per OWRI, following OFPBDS Business Rules, i.e., “20071000”. 3. Change attribute data for the new (copied) feature: a. fpbOFtrID and fpbOSiteID new features use the Site ID number (if available) or the OWEB Project Number if there is no SiteID number. If there is more than one feature for a Project, add a suffix, i.e., -A, -B for multiple features. b. fpbONm = “OWEB” c. fpbFPasSta = “Passable” d. fpbStaEvDt = CompleteYear and CompleteMonth fields per OWRI, following OFPBDS Business Rules. e. fpbStaEvMd = ”ByDesign” f. fpbOrYr = CompleteYear field per OWRI g. fpbFtrTy or fpbFtrNm if relevant, i.e. culvert replaced with bridge. h. Delete (make null) or update old information, copied from the original record, that is not related to the new feature, i.e. culvert subtype, height, length, width, slope, drop, and any other pertinent fields. i. Note: If you copied an OFPBDS feature that already has a fpbFtrID and fpbSiteID, these will need to be deleted (made null) and the Data Steward will assign new IDs. Modified Barriers If the barrier was modified, retrofitted, or improved in some manner, several fields in the OFPBDS records will be updated and the fields fpbModTy and/or fpbModDesc, in the version1_fields Table will be completed. 1. fpbModDt = CompleteYear and CompleteMonth field information from OWRI, following Business Rules for Dates. 2. fpbFPasSta = “Passable” Note: many modifications may only moderately improve passage; i.e., an upgrade from Blocked to Partial; so check OWRI comment fields or consider biologist verification if there is a question. 3. fpbStaEvDt = CompleteYear and CompleteMonth fields per OWRI, following Business Rules. 4. fpbStaEvMd = ”ByDesign” 5. fpbPasONm = “OWEB” 6. Populate the fbpModTy and/or fpbModDesc fields as appropriate: Baffles, StreamSim, Weirs, Other, Unknown. If “Other”, describe in the fpbModDes field. This might entail copying information from the OWRI comments or description fields. Issues with OWRI data - In cases where multiple passage barrier features were addressed as part of a single restoration project, especially where different types of features were addressed, it may be unclear which point represents which feature. - A large number of OWRI passage project locations have poor positional accuracy, in particular with records created with the StreamNet Event Mapper (~2005 or earlier). This issue hinders reconciliation with OFPBD, but it likely accounts for only a small percentage of the mismatches between OWRI and the current OFPBDS. OWRI records with a location confidence rating of “high” match up with OFPBD at the same rate (~15-20%) as those records with medium and low location confidence ratings. - All OWRI passage project records should be incorporated into OFPBD at a later date to maximize its comprehensiveness. There are numerous records in OWRI that are unlikely to be submitted to OFPBD by their ultimate originators because they fall on private industrial and private non-industrial forestlands. Incorporating OWRI records into OFPBD will update the database on passage problems already addressed. - Rules and assumptions for populating required attributes such as passage status (e.g. all OWRI passage projects now pass fish) will need to be developed when OWRI feature points are incorporated into the OFPBDS data. Jon Bowers Oregon Dept. of Fish and Wildlife GIS Coordinator Jon Bowers 4034 Fairview Industrial Dr SE Salem Oregon 97302 jon.k.bowers@state.or.us 503-947-6097 Jon Bowers Oregon Water Resources Department Dam Inventory Data Oregon Dept. of Fish and Wildlife - Aquatic Inventory Project Habitat Unit Level Survey Data Converted Oregon Department of Fish and Wildlife Aquatic Inventories Project (AIP) Habitat Unit data into the Oregon Fish Passage Barrier Data Standard (OFPBDS) format and loaded the data into the OFPBDS geodatabase. The ODFW Aquatic Inventories Project Habitat Unit data exists in ArcInfo Coverages packaged as Arc interchange files (.e00), last updated in 2010. Downloaded interchange files were imported into coverages in ArcCatalog, and then converted to geodatabase feature classes. A process for deriving barrier feature points from the AIP Habitat Unit line features and a crosswalk between the AIP Habitat Unit line data and OFPBDS attributes and attribute values was developed. ODFW staff, who compile the AIP Habitat Unit data, was consulted regarding deriving features and the crosswalk. OFPBDS fields were then added to the AIP Habitat Unit barrier feature tables and attribute values were populated in the OFPBDS fields. AIP Habitat Unit barrier data was then analyzed for duplication with OFPBDS records. Where AIP Habitat Unit line feature derived barrier records were duplicates of OFPBDS features, the AIP Habitat Unit barrier features were not added to the OFPBDS geodatabase. Where there was a definitive match between features, absent attribute information was migrated from the AIP Habitat Unit record to the OFPBDS feature in order to retain it. ODFW is noted as the data source for those fields. Spatial proximity along with attribute similarity was used to identify potential - and likely - duplicates. The threshold distance default was 150 meters. Points greater than 150 meters from a current OFPBDS feature location were considered new features and added. Features within 150 meters of OFPBDS features were considered potential duplicates, based on spatial proximity. Features which were potential duplicates due to proximity were compared by key attributes: feature type, stream name, road name, height, width and length. AIP Habitat Unit barrier features were also analyzed for duplication with the Oregon Watershed Enhancement Board's (OWEB) Oregon Watershed Restoration Inventory (OWRI). Where a match could be made between an OWRI record and an AIP Habitat Unit barrier feature, updates were made to pertinent fields. In February 2011, the AIP Habitat Unit barrier data were loaded into the OFPBDS enterprise geodatabase. Specific notes regarding the AIP Habitat Unit barrier feature data: * The coordinate system of the spatial coordinates in the fpbLong and fpbLat fields is GCS_North_American_1983. * The AIP Habitat Unit feature class is attributed line features for surveyed watercourses within the state. The geodatabase table contains a Unit Type field that identifies culvert crossings, artificial step structures and natural bedrock step features, i.e. waterfalls, along with a unique identifier field (HABUNT). To derive point barrier features, ODFW selected records with a Unit Type field value equal to these unit types [culvert crossings, steps created by structures, natural bedrock steps greater than 2 meters]. The Comment Code and Note fields also identified features such as dams, fish ladders and road fords. Points were generated from the selected record lines with the Feature Vertices to Points script/toolbox for line segments, using the start point of the line. Line attributes transferred to the point. *Fish passage status evaluations are based on coarse passage criteria relative to the feature type. For culverts, a drop or perch height over 0.5 feet = Partial; if the drop is equal to or greater than one foot, then a two foot or greater unit depth is needed immediately downstream (jump pool). If the downstream unit depth is equal to or greater than two feet, then the Fish Passage Status remains as "Partial". If the downstream unit depth is less than two feet, the Fish Passage Status = Blocked. If the slope of a culvert > 5% = Partial; if the drop > 3.2 feet = Blocked . For dams and other artificial step structures - if the Height > 0.5 foot = Partial; Height > 6.6 feet = Blocked; If the height is equal to or greater than one foot, then a two foot or greater unit depth is needed immediately downstream (jump pool). If the downstream unit depth is equal to or greater than two feet, then the Fish Passage Status remains as "Partial". If the downstream unit depth is less than two feet, the Fish Passage Status = Blocked. For natural features if the height is over 16 feet = Blocked. If the height is less than 16 feet = Unknown; if the slope is greater than or equal to 16 % over a distance of 200 meters = Blocked. Passage status for some barriers is unknown at this time. Consequently, some of these barriers may be completely passable to most if not all the species and life stages that have a need to migrate through the affected stream reach. * Project survey dates range from 1990 to 2009. Where data was seasonal, winter data was not used. * AIP Habitat Unit data exists on hydrographic line work generally at a scale of 1:100,000. Where there is a stream identifier (fpbStrID), and/or stream measure (fpbStrMeas) data are linear-referenced to the 1:24,000-scale PNW Framework Hydrography. AIP Habitat Unit data is available online: http://oregonstate.edu/dept/ODFW/freshwater/inventory/habitgis.html Jon Bowers Oregon Dept. of Fish and Wildlife GIS Coordinator Jon Bowers 4034 Fairview Industrial Dr SE Salem Oregon 97302 jon.k.bowers@state.or.us 503-947-6097 Jon Bowers Reconciled barrier features duplicated in the Oregon Fish Passage Barrier Data Standard (OFPBDS) geodatabase. Duplication Analysis Phase The Duplication Analysis phase consists of a set of procedures to determine if duplication exists between the targeted data and the OFPBDS. The Duplication Analysis occurs after the crosswalk methodology is approved, and the data is converted accordingly. Proximity is the most effective indicator in determining duplication, followed by a thorough, manual quality assurance review by GIS Analyst that considers attribute values and other factors such as data currency and completeness of the source datasets. The Duplication Analysis processing steps are as follows: 1) Build a Workstation (MXD): Using ArcMap, create a MXD (Map document) to house all of the data necessary to perform the Duplication Analysis. A group of datasets are required for the proximity analysis (model), and manual analysis (basemap data). a) Model Datasets: The three datasets required to run the duplication analysis model include: (1) Targeted Barriers, (2) OFPBDS, and a (3) Study Area. The targeted barriers are barriers of interest scheduled to be added to the standard, and the OFPBDS is the most recent updated version of the standard. The Study area is a polygon file that completely surrounds the targeted barriers, and can either be generated from hydrologic unit codes, or any boundary data that encompasses all targeted barriers. It is recommended to make addition modifications to the study area to tightly encompass the targeted barriers. b) Manual Datasets: The datasets instrumental in the manual analysis include: Streams (complete watercourse layer), roads (combination of BLM highways and roads), Image Web Server (Oregon Explorer), ESRI Topography (ESRI Map Server), ESRI Imagery World 2D (ESRI Map Server). These basemap datasets assist in determining apparent or ‘potential’ barrier locations. For instance, the barriers of concern for these efforts are on fish bearing streams, and in most cases, at the intersections of roads and streams. The two sets of satellite imagery shares a number of aerial indicators including: roads, streams, drainages, pools, linear vegetation indicating streams, infrastructure, and even the barriers themselves. The Topography layer helps identify slope, aspect, drainages, infrastructure, streams, roads and elevation. All together, these datasets present a strong representation of where barriers are ‘most likely’ located. 2) Run the Model: The Duplication Analysis Model (DAM) is designed to assist in the identification of duplication between barriers scheduled for integration in to the OFPBDS, and barriers that already exist in the OFPBDS. The primary goal of DAM is to distinguish between unlikely and potential duplicates in the Targeted Barriers. The unlikely duplicate barriers will be directly integrated in to the OFPBDS; where as the potential duplicates will require further investigation and analysis. a) DAM Parameters: There are three model parameters necessary to execute DAM indicated by a blue oval. These parameters include the Targeted Barriers, the OFPBDS dataset, and the custom Study Area. b) Model Assumptions / Limitations: The DAM does pose some limitations and assumptions that need to be addressed. 1) Assumption 1: DAM classifies duplicates automatically as a standalone tool. DAM is not the sole tool to identify duplication; its intention is to assist the GIS Analyst in the Duplication Analysis Process by providing a platform for further analysis with enhanced capabilities (filtered datasets, UIDs, relationship and connectivity potential, and distance measurements). 2) Assumption 2: The datasets (OFPBDS & Target Barriers) are geographically accurate. There may be unique instances where barrier features are not accurate, resulting in a false duplicate, or no duplicate at all. The Analyst Duplication Assessment will legitimize these features based upon attribute comparison, if their identified as a duplicate feature. 3) Assumption 3: The closest feature from the Target Barrier is a duplicate. In some cases, there is a duplicate, while in others there may not be. If there is a duplicate, it’s not always the closest barrier. The Model was designed to accommodate this situation, by clipping all features within 150 meters of the features as a base to run the Near Analysis. The Analyst Duplication Assessment would pick up these instances based on attribute comparison, geospatial patterns, and remote sensing using the available base map data. 4) Limitation 1: Horizontal accuracy of a feature needs to be taken in to account when comparing potential duplicates. For instance, the location accuracy of a feature may be outside of the established potential duplication range of 150 meters. 5) Limitation 2: Potential duplication is derived entirely geospatially using proximity. It does not account for similar or disparate descriptive attribute data to determine potential duplication. c) DAM Operations: There are four geospatial operations within DAM indicated by yellow boxes. First, DAM clips the OFPBDS features to the Study Area (clip). This provides a comprehensive OFPBDS copy to examine in future analysis. Next, DAM designates a 150 meter buffer around the Target Barriers (buffer), and clips the OFPBDS barriers to this buffer layer (clip 2), which results in an OFPBDS_Clipped dataset with only OFPBDS features within 150 meters of the Target Barriers. Finally, DAM performs an analysis on the Target_Barriers by calculating their distance from the closest OFPBDS_Improve barriers (near), and its corresponding ObjectID. The distance and ObjectID are added to two fields in the Target_Barriers. Note* The OFPBDS_Clipped dataset’s name will change to OFPBDS_Improve. This dataset will be used to improve duplicate features which reside in the OFPBDS if more comprehensive or accurate data is available. d) DAM Results: Two significant datasets are produced by DAM that requires further investigation. One is the OFPBDS_Improve, and the second is a revised Target_Barriers. Again, the OFPBDS_Improve dataset are OFPBDS features within 150 meters of the Target_Barriers. The OFPBDS_Improve is a direct result of the second clip operation in DAM. The revised Target_Barriers is the original Target_Barriers layer, although has two new fields added in the attribute table; one is named NEAR_FID, and the other NEAR_DIST. The NEAR_FID houses the ObjectID of the corresponding feature in the OFPBDS. Potentially, the tables can now be internally linked using the Object_ID field in OFPBDS_Improve, and the NEAR_FID field in the Target Barriers. This link may support relationship classes, joins, and several relate functions which can be applied for further evaluation in the manual analyst review. The OFPBDS_Improve dataset will be set aside for further analysis in the manual review. The Target_Barrier dataset can be delineated in to two subtypes. Features inside the 150 meter buffer will be extracted to a subsequent dataset called Potential_Duplicates. Features outside of the buffers range are extracted to a Barrier Final dataset, and set to be integrated to the OFPBDS. 3) Analyst Duplication Assessment: The Analyst Duplication Assessment is designed to physically sift through the Potential Barriers manually and compare their attributes to that of the OFPBDS_Improve. During this stage, it’s imperative to utilize professional judgment, while at all times protecting the integrity of the OFPBDS. The initial approach is to compare these datasets by their proximity to one another, and their descriptive barrier attributes. The Potential_Duplicates dataset is the primary dataset for evaluation in this assessment. a) Data Preparation: Using the workstation set forth in the first process, three main barrier datasets need to be added, and one created. These include the OFPBDS_Improve, Barriers_Final, and Potential_Duplication. An additional empty dataset called Questionable_Duplicates is also needed to house questionable barriers. b) Analyze Barriers: Two primary barrier datasets are necessary at this stage to identify duplication. They include the Apparent_Duplicates and OFPBDS_Improve datasets. By comparing these datasets by their proximity to one another, surrounding infrastructure, topography, vegetation, barrier measurements, hydrology, landscape, road/stream intersections, and remote sensing, a GIS Analyst can determine with a fair amount of certainty whether duplication exists. A document entitled, “Reconciling Duplicated barrier Features among Data Sources in the Oregon Fish Passage Barrier Data Standard” provides some assistance in this process. c) Decision Results: Three actions result from this process, which all derive from the Potential_Duplicates dataset. 1. Duplication is Determined = Data is placed in an Apparent_Duplicate dataset, and set aside for further analysis when comparing the datasets already established in the OFPBDS (OFPBDS_Improve). Refer to the section d of this process. 2. Duplication is Questionable = Record is cut and pasted to the Questionable_Duplicate dataset. (Corresponding Record is removed from OFPBDS_Improve) The Questionable_Duplicate dataset is provided back to their origin source for further analysis. 3. Barrier is Unique = Record is cut and pasted to the Target_Finals. (Corresponding Record is removed from OFPBDS_Improve) The Target_Finals are integrated to the OFPBDS directly upon completion. d) Update OFPBDS: The approach is to improve upon existing data residing in the OFPBDS. If duplication has been determined through the Apparent_Duplicate dataset, the attributes are compared to their corresponding barrier in the OFPBDS. If data is superior in the Apparent_Duplicates dataset, then the corresponding OFPBDS_Improve data is improved with the enhanced data. For example, if data is missing in the OFPBDS, and present from the Target barriers, the attributes in the Target Barriers are integrated to the OFPBDS. In addition, if data has been updated, such as the fish passage status (fpbFPasSta) from a previous assessment, the more current attribute data is utilized. Jon Bowers Oregon Dept. of Fish and Wildlife GIS Coordinator Jon Bowers 4034 Fairview Industrial Dr SE Salem Oregon 97302 jon.k.bowers@state.or.us 503-947-6097 Jon Bowers Benton County Calapooia Watershed Council Clackamas River Basin Council Scappoose Bay Watershed Council Santiam Watershed Council Rogue Basin Fish Access Team (RBFAT) Converted Rogue Basin Fish Access Team (RBFAT) data into the Oregon Fish Passage Barrier Data Standard (OFPBDS) format and loaded the data into the OFPBDS geodatabase. The RBFAT data exists in an Excel spreadsheet and an Access database, last updated in 2005. Spatial coordinates for RBFAT barrier features were not available, with the exception of the Bear Creek Watershed. RBFAT data for the Bear Creek Watershed exists in a point feature class shapefile. RBFAT features with no spatial coordinates were manually located on DRGs or imagery and digitized, referring to legal coordinates, river miles, and ownership in the spreadsheet and database, and Oregon Water Resources Point of Diversion database and Decree map information. A conversion outline, or crosswalk, between RBFAT and OFPBDS attributes and attribute values was developed. RBFAT members who compiled the data were consulted regarding the crosswalk. OFPBDS fields were added to the Bear Creek Watershed geodatabase and attribute values were populated in the OFPBDS fields. Bear Creek Watershed records were then loaded into the RBFAT geodatabase. The RBFAT geodatabase and RBFAT Access tables were joined on the BarrierID field and attribute values were populated in the OFPBDS fields. RBFAT data was then analyzed for duplication with OFPBDS records. Where RBFAT features were duplicates of OFPBDS features, the RBFAT features were not added to the OFPBDS geodatabase. Spatial proximity along with attribute similarity was used to identify potential - and likely - duplicates. The threshold distance default was 150 meters. Points greater than 150 meters from a current OFPBDS feature location were considered new features and added. Features within 150 meters of OFPBDS features were considered potential duplicates, based on spatial proximity. Features which were potential duplicates due to proximity were compared by key attributes: stream name, road name, culvert type, width and length. If there was still a question regarding duplication after this comparison, the feature was put aside in a separate feature class for consultation. Where there was a definitive match between a RBFAT feature and an OFPBDS feature, missing attribute information was merged from the RBFAT record to the OFPBDS record in order to retain it. RBFAT is noted as the data source for those fields. RBFAT barrier features were also analyzed for duplication with the Oregon Watershed Enhancement Board's (OWEB) Oregon Watershed Restoration Inventory (OWRI). Where a match could be made between an OWRI record and a RBFAT feature, updates were made to pertinent fields. The RBFAT data were exported in October 2010 into a replica copy of the enterprise geodatabase and posted to the OFPBDS enterprise geodatabase. Specific notes regarding the RBFAT data: * The coordinate system of the spatial coordinates in the fpbLong and fpbLat fields is GCS_North_American_1983. * Where there is stream identifier (fpbStrID), and/or stream measure (fpbStrMeas) data are linear-referenced to the 1:24,000-scale PNW Framework Hydrography. RBFAT fish passage barrier data is available online: http://www.restoretherogue.org/docs/rbfat_barrier_prioritization92703.xls Jon Bowers Oregon Dept. of Fish and Wildlife GIS Coordinator Jon Bowers 4034 Fairview Industrial Dr SE Salem Oregon 97302 jon.k.bowers@state.or.us 503-947-6097 Jon Bowers Umpqua Basin Fish Access Team (UBFAT) Converted from the Umpqua Basin Fish Access Team (UBFAT) fish passage data into the Oregon fish Passage Barrier Data Standard (OFPBDS). Geospatial and tabular data was provided by UBFAT, as well as a document entitled "Umpqua Basin Fish Access Team (UBFAT) Basin Plan." The overall process for incorporating the UBFAT data into the fish passage barrier data standard was as follows: 1. Obtain UBFAT data. 2. Develop a crosswalk between UBFAT and OFPBDS, and develop a methodology to determine which records, if not all, to include in the standard. 3. Address any issues (like unique identifiers). 4. Convert data into the standard. 5. Provide standardized data back to UBFAT (and often also provide Steward-modified intermediate data developed during standardization, especially where identifiers were manipulated). 6. Throughout the entire process, UBFAT were consulted. The Steward worked with the UBFAT data "as is". In other words, the Steward did not attempt to review, edit or 'correct' UBFAT records, locations or attributes. The goal was to get as much information into the standard as possible. Most UBFAT barrier data contain attributes which match those in the standard as well as attributes which do not exist in the standard. Throughout the process of converting UBFAT data into the OFPBDS, a series of determinations, assumptions and decisions were made. A UBFAT - OFPBDS Crosswalk (spreadsheet) was developed and contains a record of this, along with a document detailing key GIS steps in the conversion process. A duplication process was performed as the final stage of analysis and documented within the UBFAT crosswalk to determine what, if any UBFAT barriers were duplicates of pre-existing OFPBDS barriers. Using a duplication analysis model to identify potential duplicates within 150 meters, 838 of the 2242 barriers were classified as potential duplicates. Out of the 838 potential duplicates, 650 were apparent duplicates, while the remaining 188 were questionable. The 650 apparent duplicate barriers were then used to update or improve missing or erroneous data in the corresponding OFPBDS features. The entire integration process using UBFAT's fish passage barrier information resulted in 369 bridges, 1,211 culverts, 1 dams, and 11 waterfalls. The total of fish passage barrier features imported to the OFPBDS from UBFAT is 1,592 features. Jon Bowers Oregon Dept. of Fish and Wildlife GIS Coordinator Jon Bowers 4034 Fairview Industrial Dr SE Salem Oregon 97302 jon.k.bowers@state.or.us 503-947-6097 Jon Bowers Siuslaw Watershed Council Converted Siuslaw Watershed Council culvert inventory data into the Oregon Fish Passage Barrier Data Standard (OFPBDS) format and loaded the data into the OFPBDS geodatabase. Siuslaw Watershed Council culvert data exists in a point feature class shapefile, last updated in 2006. A conversion outline, or crosswalk, between Siuslaw Watershed Council and OFPBDS attributes and attribute values was developed. Siuslaw Watershed Council members who compiled the data were consulted regarding the crosswalk. U.S. Forest Service records in the Siuslaw Watershed Council data were excluded, pending receipt and review of statewide Forest Service data. OFPBDS fields were then added to the Siuslaw database and attribute values for all the point features were populated in the OFPBDS fields. The Siuslaw Watershed Council data was then analyzed for duplication with the OFPBDS (version 1) records. Duplicate features were not added to the OFPBDS. Spatial proximity along with attribute similarity was used to identify potential - and likely - duplicates. The threshold distance default was 150 meters. Points greater than 150 meters from a current OFPBDS (version 1) feature location were considered new features and added. Features within 150 meters of OFPBDS (version 1) features were considered potential duplicates, based on spatial proximity. Features which were potential duplicates due to proximity were compared by key attributes: stream name, road name, culvert type, width and length. If there was still a question regarding duplication after this comparison, the feature was put aside in a separate feature class for consultation. Where there was a definitive match between a Siuslaw Watershed Council feature and an OFPBDS (version 1) culvert feature, missing attribute information was merged from the Siuslaw Watershed Council record to the OFPBDS record in order to retain it. Siuslaw Watershed Council is noted as the data source for those fields. Siuslaw Watershed Council features were also analyzed for duplication with the Oregon Watershed Enhancement Board's (OWEB) Oregon Watershed Restoration Inventory (OWRI). Where a match could be made between an OWRI record and a Siuslaw Watershed Council feature, updates were made to pertinent fields. The Siuslaw Watershed Council data were exported in September 2010 into a replica copy of the enterprise geodatabase and posted to the OFPBDS enterprise geodatabase. Specific notes regarding the Siuslaw Watershed Council data: * The coordinate system of the spatial coordinates in the fpbLong and fpbLat fields is GCS_North_American_1983. *The passage status for many of the culverts is unknown at this time. Consequently, some of these barriers may be completely passable to most if not all the species and life stages that have a need to migrate through the affected stream reach. *The Siuslaw Watershed Council data includes features located by field surveys conducted for the Council, as well as records garnered from multiple agencies, including the U.S. Forest Service and Bureau of Land Management, the Oregon Department of Transportation and Watershed Enhancement Board, and Lane County. *Where there was a definitive match between an OFPBDS (version 1) and Siuslaw Watershed Council features, additional attribute information was merged from the Siuslaw Watershed Council record to the OFPBDS record in order to retain it. Siuslaw Watershed Council is noted as the data source for those fields. * Where there is stream identifier (fpbStrID), and/or stream measure (fpbStrMeas) data are linear-referenced to the 1:24,000-scale PNW Framework Hydrography. Siuslaw Watershed Council information is available online at http://www.siuslaw.org/ Jon Bowers Oregon Dept. of Fish and Wildlife GIS Coordinator Jon Bowers 4034 Fairview Industrial Dr SE Salem Oregon 97302 jon.k.bowers@state.or.us 503-947-6097 Jon Bowers Oregon Dept. of Forestry Converted Oregon Department of Forestry - Oregon Department of Fish and Wildlife (ODF-ODFW) Fish Presence barrier data into the Oregon Fish Passage Barrier Data Standard (OFPBDS) format and loaded the data into the OFPBDS geodatabase. ODF-ODFW Fish Presence barrier data consists of two data sets: attributed line features in an ODF Fish Presence geodatabase, last updated in June, 2010, and an Access database of culvert specifics, with location coordinates, taken from ODF-ODFW Fish Presence survey forms, compiled in 2000-2001 by the Oregon Department of Fish and Wildlife. A process for deriving barrier feature points from the ODF line features and a conversion outline, or crosswalk, between the Fish Presence line data, Fish Presence culvert database, and OFPBDS attributes and attribute values was developed. ODF and ODFW staff who compiled the Fish Presence data was consulted regarding the crosswalk. OFPBDS fields were then added to the ODF-ODFW Fish Presence barrier feature tables and attribute values were populated in the OFPBDS fields. ODF-ODFW Fish Presence barrier data was then analyzed for duplication between the two data sets and with OFPBDS records. Where ODF Fish Presence line feature derived barrier records were duplicates of Fish Presence culvert survey features, the line feature derived barrier was deleted. Where ODF-ODFW Fish Presence barrier features were duplicates of OFPBDS features, the ODF-ODFW Fish Presence barrier features were not added to the OFPBDS geodatabase. Where there was a definitive match between features, absent attribute information was migrated from the ODF-ODFW record to the OFPBDS feature in order to retain it. ODF-ODFW is noted as the data source for those fields. Spatial proximity along with attribute similarity was used to identify potential - and likely - duplicates. The threshold distance default was 150 meters. Points greater than 150 meters from a current OFPBDS feature location were considered new features and added. Features within 150 meters of OFPBDS features were considered potential duplicates, based on spatial proximity. Features which were potential duplicates due to proximity were compared by key attributes: stream name, road name, culvert type, width and length. If there was still a question regarding duplication after this comparison, the feature was put aside in a separate feature class for consultation. ODF-ODFW Fish Presence barrier features were also analyzed for duplication with the Oregon Watershed Enhancement Board's (OWEB) Oregon Watershed Restoration Inventory (OWRI). Where a match could be made between an OWRI record and an ODF-ODFW Fish Presence barrier feature, updates were made to pertinent fields. In October 2010, the ODF-ODFW Fish Presence barrier data were loaded into the OFPBDS enterprise geodatabase. Specific notes regarding the ODF-ODFW Fish Presence barrier feature data: * The coordinate system of the spatial coordinates in the fpbLong and fpbLat fields is GCS_North_American_1983. * The ODF Fish Presence feature class is attributed line features for watercourses within the state. The table contains a Barrier field to identify stream segments impacted by the presence of a fish barrier. To derive point features, ODFW selected records with a Barrier field value other than null or "None." Points were generated from the selected record lines [Barrier field value other than null or none] with the Feature Vertices to Points script/toolbox for line segments. Line segments above a barrier feature all carry the same barrier attribute; therefore upstream vertices need to be discarded. Arc direction varied in the feature class, so vertices (points) were checked manually against Fish Presence line work to identify the downstream terminus or point between stream segments with a barrier value other than null or none and segments with a none or null value. Line attributes transferred to the point. * ODF-ODFW Fish Presence survey data sources are varied, but are primarily Oregon Department of Forestry, Oregon Department of Fish and Wildlife, Federal land management agencies, private forest land owners, and private forestry consultants. Fish passage status evaluations are based on the ODF/ODFW Fish Presence Survey protocol described in Surveying Forest Streams for Fish Use. *Passage status for some barriers is unknown at this time. Consequently, some of these barriers may be completely passable to most if not all the species and life stages that have a need to migrate through the affected stream reach. * ODF Fish Presence data exists on hydrographic line work from several sources, including manually digitized watercourses. Where there is a stream identifier (fpbStrID), and/or stream measure (fpbStrMeas) data are linear-referenced to the 1:24,000-scale PNW Framework Hydrography. ODF Fish Presence data is available online: http://www.oregon.gov/ODF/GIS/fishpresence.shtml Jon Bowers Oregon Dept. of Fish and Wildlife GIS Coordinator Jon Bowers 4034 Fairview Industrial Dr SE Salem Oregon 97302 jon.k.bowers@state.or.us 503-947-6097 Jon Bowers US Bureau of Land Management Converted US Bureau of Land Management (BLM) data into the Oregon Fish Passage Barrier Data Standard (OFPBDS) format and loaded the data into the OFPBDS geodatabase. Data from six BLM districts in western Oregon were incorporated: Coos Bay, Eugene, Lakeview, Medford, Roseburg, Salem. Eleven BLM datasets were separately added into the OFPBDS geodatabase. BLM data were initially provided to the Data Steward October 2008, the geographic extents of which were typically entire BLM districts or individual resource areas. Subsequently (January - May 2009), the Data Steward obtained data from several BLM districts/resource areas, and this information was used instead of the original files. BLM data were provided in a variety of formats: GIS (shapefiles, geodatabases) and non-GIS (Access databases, Excel spreadsheets, Word documents). Tabular data (non-GIS) included both records with spatial coordinates and records without coordinates. Across BLM, there was a good level of consistency in the datasets, in terms of attributes and point collection. But, there were also substantial differences among the records, requiring that each dataset incorporated into the OFPBDS be handled individually. Not all barrier data provided to the Data Steward made it into the OFPBDS. There are three reasons for this: (a) The records are features, like cross drains (i.e., culverts not on streams), which are not on road-stream crossings. (b) The barriers are road-stream crossings not considered to be fish-bearing. (c) The datasets were provided in a non-GIS format and did not contain spatial coordinates, so the tabular information was not converted into GIS given the time constraints of the project. The overall process for incorporating BLM data into the fish passage barrier data standard was as follows: 1. Obtain BLM data. 2. Develop a crosswalk between BLM and OFPBDS, and develop a methodology to determine which records, if not all, to include in the standard. 3. Address any issues (like unique identifiers). 4. Convert data into the standard. 5. Provide standardized data back to BLM (and often also provide Steward-modified intermediate data developed during standardization, especially where identifiers were manipulated). 6. Throughout the entire process, BLM state and district staff were consulted. The Steward worked with the BLM data "as is". In other words, the Steward did not attempt to review, edit or 'correct' BLM records, locations or attributes. The goal was to get as much information into the standard as possible. Most BLM barrier data contain attributes which match those in the standard as well as attributes which do not exist in the standard. Throughout the process of converting BLM data into the OFPBDS, a series of determinations, assumptions and decisions were made. A BLM - OFPBDS Crosswalk (spreadsheet) was developed and contains a record of this, along with a document detailing key GIS steps in the conversion process. In order to standardize the data, crosswalks of each BLM dataset were developed to ensure that attributes and attribute values were properly matched. The crosswalk details how barriers were converted into the OFPBDS format. Two issues highlight the difficulty in integrating the data: unique identifiers (IDs); standardizing attribute values for fish passage status. There were several problems related to BLM records containing unique originator identifiers (IDs): a. There was not a consistent, unique identifier for barrier records among BLM districts and resource areas. b. Some BLM datasets did not contain any ID at all. c. Some BLM datasets contained records with duplicated IDs. To address these problems, the Steward developed a system whereby a prefix (e.g., "BLMMed" for BLM - Medford District) was added to the ID provided by BLM, or if there was no unqiue ID, the ID was modified or generated by the Steward. As for fish passage status, the OFPBDS considers barriers to be Blocked (not passable), Partial (partially passable), Passable, or Unknown. Where passage status was indicated, BLM data utilized several criteria/definitions: a. professional judgment, b. culvert design criteria, c. coarse screen filter (Green, Grey, Red). Crosswalking passage status can be less than exact (e.g where a coarse screen filter result = Red that could either equate to a partial or completely blocked culvert. In version 3 of the OFPBDS published dataset, BLM data based on a coarse screen filter result of red have been reclassified with a passage status of "partial" with the exception of culverts with drops > 3.2 feet which had a passage status of "blocked" maintained. Specific notes regarding the BLM data (for all source datasets): * The coordinate system of the spatial coordinates in the fpbLong and fpbLat fields is GCS_North_American_1983. * Most BLM datasets included BLM and non-BLM 'culverts', especially private barriers. * Values for road name (fpbRdNm) were provided by BLM, and tended to reflect BLM's internal road IDs. * Values for stream name (fpbStrNm) were provided by BLM; the source of the stream name varies. Specific notes regarding the BLM data (for one - or more - source datasets): * For fish passage status (fpbFPasSta), some BLM datasets utilized a BLM coarse filter to assess passage status while other BLM datasets utilized culvert design specifications ('Fish Pass'). The following represents how these attribute values were crosswalked to the OFPBDS values: BLM Coarse Filter OFPBDS Green Passable Grey Unknown Red Blocked BLM 'Fish Pass' OFPBDS Yes Passable No Blocked Jon Bowers Oregon Dept. of Fish and Wildlife GIS Coordinator Jon Bowers 4034 Fairview Industrial Dr SE Salem Oregon 97302 jon.k.bowers@state.or.us 503-947-6097 Jon Bowers Washington County Converted Washington County fish passage assessment culvert data into the Oregon Fish Passage Barrier Data Standard (OFPBDS) format and loaded the data into the OFPBDS geodatabase. The Washington County culvert data exists in an Excel spreadsheet, last updated in 2006 for the Dairy Creek watershed and in 2008 for the Gales Creek Watershed. A conversion outline, or crosswalk, between Washington County and OFPBDS attributes and attribute values was developed. Washington County staff who compiled the data was consulted regarding the crosswalk. OFPBDS fields were then added to the Washington County records and attribute values for all barrier features were populated in the OFPBDS fields. Washington County data was then analyzed for duplication with the OFPBDS records. Where Washington County fish barrier features were duplicates of OFPBDS features, the Washington County fish barrier feature replaced the OFPBDS feature. Spatial proximity along with attribute similarity was used to identify potential - and likely - duplicates. The threshold distance default was 150 meters. Points greater than 150 meters from a current OFPBDS feature location were considered new features and added. Features within 150 meters of OFPBDS (version 1) features were considered potential duplicates, based on spatial proximity. Features which were potential duplicates due to proximity were compared by key attributes: stream name, road name, culvert type, width and length. If there was still a question regarding duplication after this comparison, the feature was put aside in a separate feature class for consultation. Washington County barrier features were also analyzed for duplication with the Oregon Watershed Enhancement Board's (OWEB) Oregon Watershed Restoration Inventory (OWRI). Where a match could be made between an OWRI record and a Washington County feature, updates were made to pertinent fields. The Washington County data were exported in October 2010 into a replica copy of the enterprise geodatabase and posted to the OFPBDS enterprise geodatabase. Specific notes regarding the Washington County fish passage culvert data: * The coordinate system of the spatial coordinates in the fpbLong and fpbLat fields is GCS_North_American_1983. * Culverts smaller than 15 inches in diameter were excluded from the Washington County fish passage assessment as were culverts carrying streams with gradients over 15%. * The culvert survey measured four surrogate indicators to determine a culvert's ability to pass fish: culvert gradient, stream bankfull width, inlet blockage, and outlet perch. The survey method selected was based on the BLM's Fish Passage Through Road Crossing Assessment. Barrier severity determination was based on the BLM Coarse Screen Filter Version 2.2 The filter identifies a culvert's barrier level based on the requirements of juvenile salmonids. *Passage status for a number of culverts was undetermined at the time data were integrated. These culverts require additional analysis that Washington County intends to undertake, to determine their fish passage status. Consequently, these barriers may completely or partially pass most if not all the species and life stages that have a need to migrate through the affected stream reach. * Where there is stream identifier (fpbStrID), and/or stream measure (fpbStrMeas) data are linear-referenced to the 1:24,000-scale PNW Framework Hydrography. The Diary Creek Watershed Study is available online: http://www.co.washington.or.us/LUT/Divisions/Operations/upload/fishpr07.pdf Jon Bowers Oregon Dept. of Fish and Wildlife GIS Coordinator Jon Bowers 4034 Fairview Industrial Dr SE Salem Oregon 97302 jon.k.bowers@state.or.us 503-947-6097 Jon Bowers Nez Perce Tribe Converted Wallowa County BPA/Nez Perce fish barrier inventory data into the Oregon Fish Passage Barrier Data Standard (OFPBDS) format and loaded the data into the OFPBDS geodatabase. Wallowa County BPA/Nez Perce fish barrier data exists in an Excel spreadsheet, last updated in 2007. A conversion outline, or crosswalk, between Wallowa County BPA/Nez Perce and OFPBDS attributes and attribute values was developed. Wallowa County BPA/Nez Perce staff who compiled the data was consulted regarding the crosswalk. OFPBDS fields were then added to the Wallowa County BPA/Nez Perce fish barrier database and attribute values for all the point features were populated in the OFPBDS fields. The Wallowa County BPA/Nez Perce fish barrier data was then analyzed for duplication with the OFPBDS (version 1) records. Where Wallowa County BPA/Nez Perce fish barrier features were duplicates of OFPBDS (version 1) features, the Wallowa County BPA/Nez Perce fish barrier feature replaced the OFPBDS (version 1) feature. Spatial proximity along with attribute similarity was used to identify potential - and likely - duplicates. The threshold distance default was 150 meters. Points greater than 150 meters from a current OFPBDS (version 1) feature location were considered new features and added. Features within 150 meters of OFPBDS (version 1) features were considered potential duplicates, based on spatial proximity. Features which were potential duplicates due to proximity were compared by key attributes: stream name, road name, feature type and subtype. Wallowa County BPA/Nez Perce fish barrier features were also analyzed for duplication with the Oregon Watershed Enhancement Board's (OWEB) Oregon Watershed Restoration Inventory (OWRI). Where a match could be made between an OWRI record and a Wallowa County BPA/Nez Perce fish barrier feature, updates were made to pertinent fields. The Wallowa County BPA/Nez Perce fish barrier data were exported in September 2010 into a replica copy of the enterprise geodatabase and posted to the OFPBDS enterprise geodatabase. Specific notes regarding the Wallowa County BPA/Nez Perce fish barrier data: * The coordinate system of the spatial coordinates in the fpbLong and fpbLat fields is GCS_North_American_1983. *The Wallowa County BPA/Nez Perce fish barrier inventory used a U.S. Forest Service/BLM Full Assessment protocol, which includes both barrier and hydraulic analysis, to evaluate fish passage status. This protocol may result in a high number of passage status evaluations = blocked. For information on the protocol, refer to Explanations and Instructions for Passage Through Road/Stream Crossings Inventory Form (Jacobson 2003) and Region 1 Fish Passage Evaluation Criteria (Jacobson 2003). * Where there is stream identifier (fpbStrID), and/or stream measure (fpbStrMeas) data are linear-referenced to the 1:24,000-scale PNW Framework Hydrography. Wallowa County BPA/Nez Perce fish barrier features information is available online at BPA Streamnet Data Store (BPA Project No. 2002-073-00). Jon Bowers Oregon Dept. of Fish and Wildlife GIS Coordinator Jon Bowers 4034 Fairview Industrial Dr SE Salem Oregon 97302 jon.k.bowers@state.or.us 503-947-6097 Jon Bowers Oregon Dept. of Fish and Wildlife - Including StreamNet Barrier Database with state and county culverts US Forest Service Oregon Department of Fish and Wildlife - Western Oregon Rearing Project Oregon Dept. of Land Conservation and Development Lower Columbia River Estuary Partnership Converted Lower Columbia River Estuary Partnership (LCREP) fish passage barrier data into the Oregon Fish Passage Barrier Data Standard (OFPBDS) format and loaded the data into the OFPBDS geodatabase. LCREP inventoried fish passage barriers in the lower Columbia River and estuary. LCREP data exists in an ArcGIS geodatabase and feature class, last updated in 2011. A conversion outline, or crosswalk, between LCREP data and OFPBDS attributes and attribute values was developed. LCREP and Oregon Department of Land Conservation and Development staff who compiled the data was consulted regarding the crosswalk. OFPBDS fields were then added to the LCREP records and attribute values for all barrier features were populated in the OFPBDS fields. LCREP data was then analyzed for duplication with the OFPBDS records. Where LCREP features were duplicates of OFPBDS features, new or updated attribute data were transferred to the OFPBDS record. Spatial proximity along with attribute similarity was used to identify potential duplicates. The threshold distance default was 150 meters. Points greater than 150 meters from a current OFPBDS feature location were considered new features and added. Features within 150 meters of OFPBDS features were considered potential duplicates, based on spatial proximity. Features which were potential duplicates due to proximity were compared by key attributes: stream name, road name, tide gate specifics. If there was still a question regarding duplication after this comparison, the feature was put aside in a separate feature class for consultation. The LCREP data were exported in December 2014 into a replica copy of the enterprise geodatabase and posted to the OFPBDS enterprise geodatabase. Specific notes regarding the LCREP data: * The coordinate system of the spatial coordinates in the fpbLong and fpbLat fields is GCS_North_American_1983. * LCREP features were found through state and local inventories and local expert knowledge, but mapped using LiDAR derived products. *Passage status for many features was undetermined at the time data were integrated. These features require additional analysis to determine their fish passage status. Consequently, they may completely or partially pass most if not all the species and life stages that have a need to migrate through the affected stream reach. * Where there was a definitive match between an LCREP feature record with fish passage status and an OFPBDS feature with unknown fish passage status, that attribute information was merged from the OFPBDS record. LCREP is noted as the data source for those fields (fpbFPasONm). Ruth Schellbach ODFW GIS Technician 4034 Fairview Industrial Dr Salem Oregon 97302 ruth.e.schellbach@state.or.us Ruth Schellbach Ruth Schellbach Converted Oregon Department of Fish and Wildlife (ODFW) fish passage barrier data into the Oregon Fish Passage Barrier Data Standard (OFPBDS) format and loaded the data into the OFPBDS geodatabase. Metadata for ODFW barrier data states the following: This dataset contains barriers to fish passage that are known to affect and potentially affect anadromous and/or resident fish migration within the state of Oregon. The following barrier types are included: dams, culverts, falls, cascade/gradient/velocity, hatchery facility-related, tide gates, debris jams, water diversions, insufficient flow, fords, bridges and weirs. The passage status attribute describes whether a barrier feature blocks passage (complete or partial blockage), is passable or has an unknown passage status. The passage status attribute, in some cases, may not reflect the current passage status of the barrier (for culverts in particular) as conditions may have changed since the date the passage status was last evaluated. The passage status for many of the barriers is unknown due to potential effects on species and/or life stages where little information exists at this time. Consequently, many of these barriers may be completely passable to most if not all the species and life stages that have a need to migrate through the affected stream reach. The dataset includes the ODFW - ODOT jointly developed "Assessment of Road Culverts for Fish Passage Problems on State and County Owned Roads" (1999). ODFW barrier data exist in an enterprise geodatabase consisting of multiple tables and one point feature class. The data were exported in June 2009 into a replica copy of the enterprise geodatabase where the records were manipulated. OFPBDS fields were added to the database. A crosswalk between ODFW and OFPBDS attributes and attribute values was developed. Once the crosswalk was completed, attribute values for all the point features were populated in the OFPBDS fields. The point features and attributes were then loaded into the OFPBDS geodatabase. A number of ODFW staff were consulted for the crosswalk. Agency staff were also involved in the standardization process. Specific notes regarding the ODFW data: * The coordinate system of the spatial coordinates in the fpbLong and fpbLat fields is GCS_North_American_1983. * For the multiple features attribute (fpbMltFtr), those records with a "yes" are features which occur at multiple-feature sites AND the features are part of multiple-feature sites which have the multiple features in the OFPBDS database. The fpbMltFtr attribute was not used to indicate features belonging to multiple-feature sites unless records for the features were actually in the database. * ODFW data are linear-referenced to the 1:24,000-scale PNW Framework Hydrography. The stream identifier (fpbStrID), stream measure (fpbStrMeas) and stream name (fpbStrNm) are dervied from the framework hydrography. * Values for road name (fpbRdNm) are what was originally inputted for the ODFW data; the source of the name varies. * A value of 0 for slope (fpbSlope) is presumed to indicate a flat plane. * A value of 0 for drop (fpbDrop) is presumed to indicate no drop. ODFW barrier data are published online at http://nrimp.dfw.state.or.us/nrimp/default.aspx?pn=fishbarrierdata. 2009-01-01T00:00:00 Jon Bowers Oregon Dept. of Fish and Wildlife GIS Coordinator Jon Bowers 4034 Fairview Industrial Dr SE Salem Oregon 97302 jon.k.bowers@state.or.us 503-947-6097 Jon Bowers Converted Oregon Department of Transportation (ODOT) culvert data into the Oregon Fish Passage Barrier Data Standard (OFPBDS) format and loaded the data into the OFPBDS geodatabase. Culvert data from ODOT's Drainage Facility Management System (DFMS) were exported into XML format and provided to the Data Steward in August 2009. The data were converted into a feature class based upon the spatial coordinates of the records and added into a geodatabase where the records were manipulated. A methodology was developed to identify which of the ODOT culvert records were culverts at stream crossings. OFPBDS fields were added to the database. A crosswalk between ODOT and OFPBDS attributes and attribute values was developed. Once the crosswalk was completed, attribute values for the selected point features were populated in the OFPBDS fields. The point features and attributes were then loaded into the OFPBDS geodatabase. Several ODOT staff were consulted for the crosswalk and the record selection methodology. Specific notes regarding the ODOT data: * The coordinate system of the spatial coordinates in the fpbLong and fpbLat fields is GCS_North_American_1983. * Features with a originator feature identifier (fpbOFtrID) beginning with "T" are temporary records and are (eventually) replaced. * Some culverts exist at multiple-feature sites. Since ODOT provided only one record per site for multiple-feature sites, the Data Steward added culvert records for these additional features. * For the multiple features attribute (fpbMltFtr), those records with a "yes" are features which occur at multiple-feature sites AND the features are part of multiple-feature sites which have the multiple features in the OFPBDS database. The fpbMltFtr attribute was not used to indicate features belonging to multiple-feature sites unless records for the features were actually in the database. Fish passage status (fpbFPasSta) for ODOT records has been assigned by ODFW using the following criteria: - where culvert drop > 1 foot and < 3.2 feet, passage status was assigned as "partial" - where culvert drop > 3.2 feet, passage status was assigned as "blocked" Fish passage status for ODOT culverts is a determination made by ODFW staff; ODOT defers to ODFW for evaluating passage status. * Values for stream name (fpbStrNm) were provided by ODOT; the source of the stream name varies. * For the road identifier (fpbRdID) and road measure (fpbRdMeas) attributes, ODOT's Highway and Milepoint attributes were used. Note that these two attributes alone are not enough to identify ODOT road features and their locations - other road attributes are needed as well. Note also that ODOT has more than one type of mileage (example: Milepoint 45 is not the same as Milepoint Z 45). fpbRdMeas is the road route measure in kilometers -- units in Milepoint were converted from miles. * A value of 0 for drop (fpbDrop) is presumed to indicate no drop 2009-08-03T00:00:00 Jon Bowers Oregon Dept. of Fish and Wildlife GIS Coordinator Jon Bowers 4034 Fairview Industrial Dr SE Salem Oregon 97302 jon.k.bowers@state.or.us 503-947-6097 Jon Bowers Data was converted from the Calapooia Watershed Council (CWC) fish passage data into the Oregon fish Passage Barrier Data Standard (OFPBDS). Geospatial and tabular data was provided by CWC, as well as a document entitled "Calapooia Watershed Fish Passage Assessment." The overall process for incorporating the CWC data into the fish passage barrier data standard was as follows: 1. Obtain CWC data. 2. Develop a crosswalk between CWC and OFPBDS, and develop a methodology to determine which records, if not all, to include in the standard. 3. Address any issues (like unique identifiers). 4. Convert data into the standard. 5. Provide standardized data back to CWC (and often also provide Steward-modified intermediate data developed during standardization, especially where identifiers were manipulated). 6. Throughout the entire process, CWC was consulted. The Steward worked with the CWC data "as is". In other words, the Steward did not attempt to review, edit or 'correct' CWC records, locations or attributes. The goal was to get as much information into the standard as possible. Most CWC barrier data contain attributes which match those in the standard as well as attributes which do not exist in the standard. Throughout the process of converting CWC data into the OFPBDS, a series of determinations, assumptions and decisions were made. A CWC - OFPBDS Crosswalk (spreadsheet) was developed and contains a record of this, along with a document detailing key GIS steps in the conversion process. A duplication process was performed as the final stage of analysis and documented within the CWC crosswalk to determine what, if any CWC barriers were duplicates of pre-existing OFPBDS barriers. Using a duplication analysis model to identify potential duplicates within 150 meters, 65 of the 116 barriers were classified as potential duplicates. Out of the 65 potential duplicates, 48 were apparent duplicates, while the remaining 17 were questionable. The 48 apparent duplicate barriers were then used to update or improve missing or erroneous data in the corresponding OFPBDS features. The entire integration process using CWC's fish passage barrier information resulted in the addition of 68 culverts. 2010-01-01T00:00:00 Jon Bowers Oregon Dept. of Fish and Wildlife GIS Coordinator Jon Bowers 4034 Fairview Industrial Dr SE Salem Oregon 97302 jon.k.bowers@state.or.us 503-947-6097 Jon Bowers Data was converted from the Clackamas River Basin Council (CRBC) fish passage data into the Oregon fish Passage Barrier Data Standard (OFPBDS). Geospatial and tabular data was provided by CRBC, as well as two documents entitled "Clear and Foster Creek Fish Passage Assessment and Prioritization Project," and "Deep, Goose and Eagle Creeks Fish Passage Assessment." The overall process for incorporating the CRBC data into the fish passage barrier data standard was as follows: 1. Obtain CRBC data. 2. Develop a crosswalk between CRBC and OFPBDS, and develop a methodology to determine which records, if not all, to include in the standard. 3. Address any issues (like unique identifiers). 4. Convert data into the standard. 5. Provide standardized data back to CRBC (and often also provide Steward-modified intermediate data developed during standardization, especially where identifiers were manipulated). 6. Throughout the entire process, CRBC was consulted. The Steward worked with the CRBC data "as is". In other words, the Steward did not attempt to review, edit or 'correct' CRBC records, locations or attributes. The goal was to get as much information into the standard as possible. Most CRBC barrier data contain attributes which match those in the standard as well as attributes which do not exist in the standard. Throughout the process of converting CRBC data into the OFPBDS, a series of determinations, assumptions and decisions were made. A CRBC - OFPBDS Crosswalk (spreadsheet) was developed and contains a record of this, along with a document detailing key GIS steps in the conversion process. A duplication process was performed as the final stage of analysis and documented within the CRBC crosswalk to determine what, if any CRBC barriers were duplicates of pre-existing OFPBDS barriers. Using a duplication analysis model to identify potential duplicates within 150 meters, 90 of the 558 barriers were classified as potential duplicates. Out of the 90 potential duplicates, 48 were apparent duplicates, while the remaining 46 were questionable. The 48 apparent duplicate barriers were then used to update or improve missing or erroneous data in the corresponding OFPBDS features. The entire integration process using CRBC's fish passage barrier information resulted in the addition of 469 culverts. 2010-01-01T00:00:00 Jon Bowers Oregon Dept. of Fish and Wildlife GIS Coordinator Jon Bowers 4034 Fairview Industrial Dr SE Salem Oregon 97302 jon.k.bowers@state.or.us 503-947-6097 Jon Bowers Jon Bowers Oregon Dept. of Fish and Wildlife GIS Coordinator Jon Bowers 4034 Fairview Industrial Dr SE Salem Oregon 97302 jon.k.bowers@state.or.us 503-947-6097 Jon Bowers Converted Oregon Water Resources Department Dam Inventory data into the Oregon Fish Passage Barrier Data Standard (OFPBDS) format and loaded the data into the OFPBDS geodatabase. Metadata for OWRD dam data states the following: dams within the jurisdiction of Oregon Water Resource Department are defined by a dam height >= 10 feet and storage of >= 9.2 acre feet. OWRD dam data exist in an enterprise geodatabase as a point feature class, updated in June 2010, and a SQL database with ongoing updates. A geodatabase with a point feature class and an Excel Spreadsheet of 318 additional dams, were provided to the Data Steward in June and July 2010 respectively. A feature class was created for the Excel spreadsheet records by importing the spatial coordinates through ArcGIS. The two feature classes were checked for record duplication and then merged. A crosswalk between OWRD and OFPBDS attributes and attribute values was developed. Additionally, a methodology was developed to identify OWRD dam records that were not located in stream channels, i.e. waste water lagoons, and therefore not a fish passage barrier. OWRD staff was consulted for the crosswalk and the record selection methodology. Once the crosswalk was completed, OFPBDS fields were added to the database and attribute values for all the point features were populated in the OFPBDS fields. The data were exported in July 2010 into a replica copy of the enterprise geodatabase. Once the dam features were loaded in the OFPBDS replica, the data were analyzed for duplication. Where OWRD features were duplicates of OFPBDS (version 1) features, the OWRD dam feature replaced the OFPBDS (version 1) dam feature. Spatial proximity along with attribute similarity was used to identify potential - and likely - duplicates. The threshold distance default was 150 meters. However, upon visual inspection of the distance between OWRD and OFPBDS (version 1) dam features with matching attribute characteristics, some were over 2,000 feet apart. Potential duplicates, based on spatial proximity, were manually reviewed to identify those which were actual (confirmed) duplicates. Features which were potential duplicates due to proximity were compared by key attributes: Dam name, stream name, dam height, and owner. If there was still a question regarding duplication after this comparison, OWRD's water rights database was queried. Because OWRD does not collect information on fish passage status, where there was a definitive match between an OWRD dam record and an OFPBDS (version 1) dam feature with barrier status and fishway information, that attribute information was merged from the OFPBDS record to the OWRD record in order to retain it. ODFW is noted as the data source for those fields (fpbFPasONm). A second manual review based on feature name similarity further identified actual duplicates where feature points were greater than 150 meters apart. Dam features removed from the OFPBDS (version 1) database were ODFW records. Once the barrier features were compiled in the OFPBDS database and once features were analyzed for duplication, a limited effort was made to update dam features based upon the Oregon Watershed Enhancement Board's (OWEB) Oregon Watershed Restoration Inventory (OWRI). The point features and attributes were then loaded into the OFPBDS geodatabase. Specific notes regarding the OWRD dam data: * The coordinate system of the spatial coordinates in the fpbLong and fpbLat fields is GCS_North_American_1983. *The passage status for many of the dams is unknown at this time. Consequently, some of these barriers may be completely passable to most if not all the species and life stages that have a need to migrate through the affected stream reach. *Because OWRD does not collect information on fish passage status, where there was a definitive match between an OWRD dam record and an OFPBDS (version 1) dam feature with barrier status and fishway information, that attribute information was merged from the OFPBDS record to the OWRD record in order to retain it. ODFW is noted as the data source for those fields (fpbFPasONm). *Values for stream name (fpbStrNm) were provided by OWRD and are generally the storage water source as stated on the OWRD permit, not the location of the dam relative to a stream channel. * Where there is stream identifier (fpbStrID), and/or stream measure (fpbStrMeas) data are linear-referenced to the 1:24,000-scale PNW Framework Hydrography. 2010-01-01T00:00:00 Jon Bowers Oregon Dept. of Fish and Wildlife GIS Coordinator Jon Bowers 4034 Fairview Industrial Dr SE Salem Oregon 97302 jon.k.bowers@state.or.us 503-947-6097 Jon Bowers Converted the Scappoose Bay Watershed Council's (SBWC) fish passage data into the Oregon fish Passage Barrier Data Standard (OFPBDS). Geospatial and tabular data was provided by SBWC, as well as a document entitled "A comprehensive Assessment of Fish Passage Barriers in the Scappoose Bay Watershed." The overall process for incorporating SBWC data into the fish passage barrier data standard was as follows: 1. Obtain SBWC data. 2. Develop a crosswalk between SBWC and OFPBDS, and develop a methodology to determine which records, if not all, to include in the standard. 3. Address any issues (like unique identifiers). 4. Convert data into the standard. 5. Provide standardized data back to SBWC (and often also provide Steward-modified intermediate data developed during standardization, especially where identifiers were manipulated). 6. Throughout the entire process, SBWC were consulted. The Steward worked with the SBWC data "as is". In other words, the Steward did not attempt to review, edit or 'correct' SBWC records, locations or attributes. The goal was to get as much information into the standard as possible. Most SBWC barrier data contain attributes which match those in the standard as well as attributes which do not exist in the standard. Throughout the process of converting SBWC data into the OFPBDS, a series of determinations, assumptions and decisions were made. A SBWC - OFPBDS Crosswalk (spreadsheet) was developed and contains a record of this, along with a document detailing key GIS steps in the conversion process. A duplication process was performed as the final stage of analysis to determine what, if any SBWC barriers were duplicates of pre-existing OFPBDS barriers. It was determined using a 150 meter distance analysis that 13 barriers had in fact already existed in the OFPBDS dataset. In comparing the two, it was determined that the 13 newer SBWC contained more comprehensive and updated data, and subsequently, the 13 records were removed in the OFPBDS, and replaced by the SBWC records. The entire integration process using SBWC's fish passage barrier information resulted in 1 bridge, 96 culverts, 12 dams, and 1 tidegate. The total of fish passage barrier features imported to the OFPBDS from SBWC is 110 features. 2010-01-01T00:00:00 Jon Bowers Oregon Dept. of Fish and Wildlife GIS Coordinator Jon Bowers 4034 Fairview Industrial Dr SE Salem Oregon 97302 jon.k.bowers@state.or.us 503-947-6097 Jon Bowers Data was integrated from the Santiam Watershed Council's (Santiam WC) fish passage data into the Oregon fish Passage Barrier Data Standard (OFPBDS). Geospatial and tabular data was provided by Santiam WC. The overall process for incorporating the Santiam data into the fish passage barrier data standard was as follows: 1. Obtain Santiam WC data (107 records). 2. A crosswalk was not necessary for Santiam WC because they used ODFW's schema and existing barriers. 3. Santiam WC updated and corrected attributes of these existing fish passage barriers, most importantly, barrier dimensions and fish passage status. 4. Where Santiam WC identified multiple features at a single location, fish passage barriers records were added. Exactly 18 barriers were added, and assigned Santiam WC as the fish passage barrier originator (fpbOrNm). The remaining features retained ODFW as their original source. 5. Provide standardized data back to Santiam WC (and often also provide Steward-modified intermediate data developed during standardization, especially where identifiers were manipulated). 6. Throughout the entire process, Santiam WC was consulted. The Steward worked with the Santiam WC data "as is". In other words, the Steward did not attempt to review, edit or 'correct' Santiam WC records, locations or attributes. The goal was to get as much information into the standard as possible. Most Santiam WC barrier data contain attributes which match those in the standard as well as attributes which do not exist in the standard. The entire integration process using Santiam WC's fish passage barrier information resulted in the addition of 18 culverts. 2010-01-01T00:00:00 Jon Bowers Oregon Dept. of Fish and Wildlife GIS Coordinator Jon Bowers 4034 Fairview Industrial Dr SE Salem Oregon 97302 jon.k.bowers@state.or.us 503-947-6097 Jon Bowers Converted Benton County's fish passage data into the Oregon fish Passage Barrier Data Standard (OFPBDS). Geospatial and tabular data was provided by BENTON COUNTY, as well as a document entitled "A comprehensive Assessment of Fish Passage Barriers in the Scappoose Bay Watershed." The overall process for incorporating Benton County's data into the fish passage barrier data standard was as follows: 1. Obtain Benton County data. 2. Develop a crosswalk between Benton County and OFPBDS, and develop a methodology to determine which records, if not all, to include in the standard. 3. Address any issues (like unique identifiers). 4. Convert data into the standard. 5. Provide standardized data back to Benton County (and often also provide Steward-modified intermediate data developed during standardization, especially where identifiers were manipulated). 6. Throughout the entire process, Benton County was consulted. The Steward worked with the Benton County data "as is". In other words, the Steward did not attempt to review, edit or 'correct' Benton County records, locations or attributes. The goal was to get as much information into the standard as possible. Most Benton County barrier data contain attributes which match those in the standard as well as attributes which do not exist in the standard. Throughout the process of converting Benton County data into the OFPBDS, a series of determinations, assumptions and decisions were made. A Benton County - OFPBDS Crosswalk (spreadsheet) was developed and contains a record of this, along with a document detailing key GIS steps in the conversion process. A duplication process was performed as the final stage of analysis and documented within the Benton County crosswalk to determine what, if any Benton County barriers were duplicates of pre-existing OFPBDS barriers. Using a duplication analysis model to identify potential duplicates within 150 meters, 93 of the 571 barriers were classified as potential duplicates. Out of the 93 potential duplicates, 60 were apparent duplicates, while the remaining 33 were questionable. The 60 apparent duplicate barriers were then used to update or improve missing or erroneous data in the corresponding OFPBDS features. The entire integration process using Benton County's fish passage barrier information resulted in 224 bridges, 2 cascades, 219 culverts, 5 dams, 4 waterfalls, 2 fords, 1 weir, 4 other known fish passage barrier feature including debris jams, and 13 unknown features. The total of fish passage barrier features imported to the OFPBDS from Benton County is 474 features. 2010-01-01T00:00:00 Jon Bowers Oregon Dept. of Fish and Wildlife GIS Coordinator Jon Bowers 4034 Fairview Industrial Dr SE Salem Oregon 97302 jon.k.bowers@state.or.us 503-947-6097 Jon Bowers United States Forest Service (USFS) Culvert Inventory data were converted into the Oregon Fish Passage Barrier Data Standard (OFPBDS) format and loaded into the OFPBDS geodatabase. Data were obtained from the following National Forests: Deschutes, Fremont - Winema, Malheur, Mt. Hood, Ochoco, Rogue River - Siskiyou, Siuslaw, Umatilla, Umpqua, Wallowa Whitman, and Willamette. Point feature classes were provided from each of the forests giving culvert locations and a varying amount of attribute data. Additional attribute data from two regional datasets were used to augment the attributes furnished by the forests. A file geodatabase was constructed for each forest to contain the source spatial and tabular data and the derived data products. The number of records per forest varied from 40 to over 400, and the total number of records processed was 3,046. A crosswalk between USFS and OFPBDS attributes and attribute values was developed for each forest. The crosswalk consists of three sections: a section that contains summary information relating to the entire dataset; a section for “Required” attributes, which provide information considered essential to the usefulness of the data; and a section for “Optional” attributes, which provide supplementary information that provide additional details not found in the required attributes . An initial crosswalk was developed and sent to each forest presenting the mapping between USFS attributes and OFPBDS attributes and describing the processing necessary to transform the USFS data to meet OFPBDS standards. Each forest was invited to review the crosswalk and submit comments or concerns related to the proposed processing of their data. Processing the data from each forest took place in four primary phases executed sequentially. The objective of the processing was to identify and upload fish passage barriers in the forest data that were not yet represented in the OFPBDS dataset and to update existing records with more current information coming from the forests. The first phase of the processing established a correspondence between the USFS data and the OFPBDS data such that USFS attributes were transformed to meet the standards set forth in the Oregon Fish Passage Barrier Data Standard document. The resulting attribute values were loaded into empty “Required” and “Optional” fields corresponding to the OFPBDS attributes appended to each record in the USFS point feature class. The next phase of processing compared fish passage barrier point features in the USFS data to existing features in the OFPBDS dataset. Spatial proximity along with attribute similarity were used to identify potential and likely duplicates. A default threshold distance of 150 meters was used to partition the USFS points into those too distant from any OFPBDS point to be considered to represent the same feature and those close enough to be potential duplicates. Taking the potential duplicates, a script was run that compares the values of selected attributes and considers spatial proximity to calculate a measure of how much evidence exists in the data to indicate duplicate points. A summary table was constructed to permit quick comparisons of attribute pairs and see the cause of a mismatch. Where the evidence was low, a close manual examination of the pair of points in ArcGIS was conducted to confirm whether they represent the same or different features. Where the evidence for matched points was high, e.g. points less than 30 meters apart, a quick look was usually sufficient to confirm the match. In order to obtain additional information that might clarify the status of culverts that had been removed or replaced, a second proximity analysis was run against the Oregon Watershed Enhancement Board’s (OWEB) Oregon Watershed Restoration Inventory (OWRI). The same threshold of 150 meters was used, and OWRI points close to USFS points were manually examined to determine if any recent maintenance action may have affected the status of the culvert. The third phase of processing the data involved linearly referencing the new USFS points to be added to the OFPBDS dataset. Each new point was spatially analyzed to determine where it falls on a mapped stream. The Framework hydrography dataset was used to reference each barrier point, assign a unique stream identifier and stream distance measure. The final phase in the processing consisted of a quality check on the new data points prior to loading the data into the OFPBDS dataset. In the case of USFS barriers that were already represented in the OFPBDS data, a check was performed to determine if the USFS data contained new fish passage information. If so, the fish passage status (fpbFPasSta), fish passage data originator (fpbFPasONm), and revision date (fpbRevDt) were updated in the OFPBDS dataset. For new fish passage barrier records, the data were loaded into an editable version of the OFPBDS dataset, which was uploaded to a QA version and verified before being incorporated into the operational version. Specific notes regarding USFS fish passage barrier data: There was a wide variation in the quantity and quality of the initial datasets obtained from the forests. The number of attributes varied from less than 20 to well over 100. Approximately half of the datasets were well-attributed, while a few had most of the “Required” attributes and some of the “Optional”, and the remaining datasets did not have many of either category of attribute. To supplement the attributes supplied by the forests, the forests’ attribute tables were linked to available regional fish passage datasets, which supplied additional attributes. Two types of feature identifier schemes were employed in the USFS data. One scheme utilizes a long integer of 10 or more digits, which is unique across forests. The other scheme is basically a sequential numbering of the records from one to the total number of records. There were two ramifications of this situation. In order to connect datasets with the sequential numbering to regional data, additional attributes had to be used to achieve a unique match.. The second impact was that in order to have identifiers unique across forests, the originator feature ID (fpbOFtrID) was made to consist of a concatenation of the forest name and the identifier used within the forest. Physical data on culverts was often lacking. In many cases the basic parameters of height, width and length were absent. In other cases the values were suspect, either because they seemed to be in the wrong units or because they differed significantly from other measurements at the same location. In order to represent slopes as positive numbers, the sign had to be inverted. Drop values also were inverted to create positive numbers, but there were many instances of both positive and negative drops in the same dataset. The existence of multiple culverts, in space or over time, was usually not clearly represented. In a few instances multiple culverts were represented by multiple features in the dataset and identified as such. More commonly, the only indication of the existence of multiple features was a note in the “Comments” field. Similarly, the only indication of a culvert replacement or removal was often in the form of a cursory note, making it difficult to determine whether the data in the current record represented a culvert that had been taken out or one that replaced it. 2012-01-02T00:00:00 Jon Bowers Oregon Dept. of Fish and Wildlife GIS Coordinator Jon Bowers 4034 Fairview Industrial Dr SE Salem Oregon 97302 jon.k.bowers@state.or.us 503-947-6097 Jon Bowers Jon Bowers Oregon Dept. of Fish and Wildlife GIS Coordinator Jon Bowers 4034 Fairview Industrial Dr SE Salem Oregon 97302 jon.k.bowers@state.or.us 503-947-6097 Jon Bowers Converted Oregon Department of Land Conservation and Development (DLCD) tide gate data into the Oregon Fish Passage Barrier Data Standard (OFPBDS) format and loaded the data into the OFPBDS geodatabase. DLCD compiled a non-comprehensive inventory of tide gates in major estuaries along the Oregon coast, that protect lowlands from flooding. The DLCD tide gate data exists in an ArcGIS shapefile, last updated in 2011. A conversion outline, or crosswalk, between DLCD tide gate data and OFPBDS attributes and attribute values was developed. DLCD staff who compiled the data was consulted regarding the crosswalk. OFPBDS fields were then added to the DLCD records and attribute values for all barrier features were populated in the OFPBDS fields. DLCD tide gate data was then analyzed for duplication with OFPBDS records. Where DLCD tide gate features were duplicates of OFPBDS features, the DLCD feature replaced the OFPBDS feature. Spatial proximity along with attribute similarity was used to identify potential duplicates. The threshold distance default was 150 meters. Points greater than 150 meters from a current OFPBDS feature location were considered new features and added. Features within 150 meters of OFPBDS features were considered potential duplicates, based on spatial proximity. Features which were potential duplicates due to proximity were compared by key attributes: stream name, road name, tide gate specifics. If there was still a question regarding duplication after this comparison, the feature was put aside in a separate feature class for consultation. The DLCD tide gate data were exported in November 2014 into a replica copy of the enterprise geodatabase and posted to the OFPBDS enterprise geodatabase. Specific notes regarding the DLCD tide gate data: * The coordinate system of the spatial coordinates in the fpbLong and fpbLat fields is GCS_North_American_1983. * DLCD tide gate features were found through local inventories and local expert knowledge, but mapped tide gate location was digitized using LiDAR derived products. *Passage status for most tide gates was undetermined at the time data were integrated. These tide gates require additional analysis to determine their fish passage status. Consequently, these barriers may completely or partially pass most if not all the species and life stages that have a need to migrate through the affected stream reach. * Because DLCD does not collect information on fish passage status, where there was a definitive match between an DLCD tide gate record and an OFPBDS tide gate feature with barrier status, that attribute information was merged from the OFPBDS record to the DLCD record in order to retain it. ODFW is noted as the data source for those fields (fpbFPasONm). 2014-11-03T00:00:00 Ruth Schellbach ODFW GIS Technician 4034 Fairview Industrial Dr Salem Oregon 97302 ruth.e.schellbach@state.or.us Ruth Schellbach Transferred the BLM fish barrier data (2014) into the Oregon Fish Passage Barrier Data Standard (OFPBDS) format and loaded the data into the OFPBDS geodatabase. BLM fish barrier data (2014) exists in two feature classes in an ArcGIS file geodatabase with ofpbds schema. The BLM fish barrier data (2014) was analyzed for duplication with the OFPBDS records. Where BLM fish barrier data (2014) features were duplicates of OFPBDS features, ofpbds feature attributes were updated. Spatial proximity along with attribute similarity was used to identify potential duplicates. The threshold distance default was 150 meters. Points greater than 150 meters from a current OFPBDS feature location were considered new features and added. Features within 150 meters of OFPBDS features were considered potential duplicates, based on spatial proximity. Features which were potential duplicates due to proximity were compared by key attributes: stream name, road name, feature type and subtype. The BLM fish barrier data (2014) were exported in January 2015 into a replica copy of the enterprise geodatabase and posted to the OFPBDS enterprise geodatabase. BLM fish barrier feature information is available online at http://www.blm.gov/or/districts/prineville/plans/johndayrmp/data/data-details.php?id=278. 2014-12-01T00:00:00 Ruth Schellbach ODFW GIS Technician 4034 Fairview Industrial Dr Salem Oregon 97302 ruth.e.schellbach@state.or.us Ruth Schellbach Converted Oregon Department of Transportation Drainage Facilities Management System (DFMS) culvert data into the Oregon Fish Passage Barrier Data Standard (OFPBDS) format and loaded the data into the OFPBDS geodatabase. The DFMS data, provided in 2015, represents culverts ODOT has been able to field verify on specific highways, or highway segments, as prioritized by ODOT. It updates and refines the location, number, and description of culverts for the 27 highways/highway sections surveyed since 2007. The DFMS culvert data exists in an Excel spreadsheet. A conversion outline, or crosswalk, between DFMS and OFPBDS attributes and attribute values was developed. Oregon Department of Transportation staff who compiled the data was consulted regarding the crosswalk. OFPBDS fields were then added to the DFMS records and attribute values for all culvert features were populated in the OFPBDS fields. DFMS data was then analyzed for duplication with OFPBDS records. Where DFMS features were duplicates of OFPBDS features, the DFMS feature replaced the OFPBDS feature. Spatial proximity along with attribute similarity was used to identify potential duplicates. The threshold distance default was 100 feet. Points greater than 100 feet from a current OFPBDS feature location were further checked with a proximity analysis of 250 feet. A manual review based on stream and road name similarity further identified actual duplicates where feature points were greater than 250 feet apart. Features considered potential duplicates, based on spatial proximity were compared by key attributes: stream name, road name, culvert specifics. If there was still a question regarding duplication after this comparison, the feature was put aside in a separate feature class for consultation. Because ODOT does not collect information on fish passage status, where there was a definitive match between a DFMS feature and an OFPBDS feature with fish passage status, that attribute information was merged from the OFPBDS record to the DFMS record in order to retain it. ODFW is noted as the data source for those fields (fpbFPasONm). The Oregon Department of Transportation DFMS data were exported in May 2015 into a replica copy of the enterprise geodatabase and posted to the OFPBDS enterprise geodatabase. Specific notes regarding the DFMS culvert data: * The coordinate system of the spatial coordinates in the fpbLong and fpbLat fields is GCS_North_American_1983. * Culverts smaller than 15 inches in diameter were excluded from integration into OFPBDS, as were features characterized as road drainage culverts, serving slopes with gradients over 15 percent, fields, or drainage channels with no direct access to streams. *Because ODOT does not collect information on fish passage status, where there was a definitive match between a DFMS record and an OFPBDS feature with fish passage status, that attribute information was merged from the OFPBDS record to the DFMS record in order to retain it. ODFW is noted as the data source for those fields (fpbFPasONm). *Passage status for a number of culverts was undetermined at the time data were integrated. These culverts require additional analysis to determine their fish passage status. Consequently, these culverts may completely or partially pass most if not all the species and life stages that have a need to migrate through the affected stream reach. *ODOT DFMS stream names are local names, and may differ significantly from GNIS names for the same location. *Where there is stream identifier (fpbStrID), and/or stream measure (fpbStrMeas) data are linear-referenced to the 1:24,000-scale PNW Framework Hydrography. 2015-03-02T00:00:00 Ruth Schellbach ODFW GIS Technician 4034 Fairview Industrial Dr Salem Oregon 97302 ruth.e.schellbach@state.or.us Ruth Schellbach Converted Oregon Department of Transportation bridge and large culvert data from their PONTIS, bridge management software, into the Oregon Fish Passage Barrier Data Standard (OFPBDS) format and loaded the data into the OFPBDS geodatabase. The PONTIS data represent bridges and large culverts in Oregon, owned by the state, cities, or counties, or other owners that cross state highways. It does not include structures owned by Federal agencies. The PONTIS data exists in an ArcGIS shapefile. A conversion outline, or crosswalk, between ODOT and OFPBDS attributes and attribute values was developed. Oregon Department of Transportation staff who compiled the data was consulted regarding the crosswalk. OFPBDS fields were then added to the ODOT records and attribute values for all features were populated in the OFPBDS fields. PONTIS data was then analyzed for duplication with OFPBDS records. Where bridge and culvert features were duplicates of OFPBDS features, the ODOT feature replaced the OFPBDS feature. Spatial proximity along with attribute similarity was used to identify potential duplicates. The threshold distance default was 300 feet. Points greater than 300 feet from a current OFPBDS culvert or bridge feature were considered new features. A manual review based on stream and road name similarity further identified actual duplicates where feature points were greater than 300 feet apart. Features considered potential duplicates, based on spatial proximity were compared by key attributes: stream name, road name, culvert specifics. If there was still a question regarding duplication after this comparison, the feature was put aside in a separate feature class for consultation. Because ODOT does not collect information on fish passage status, where there was a definitive match between an ODOT feature and an OFPBDS feature with barrier status, that attribute information was merged from the OFPBDS record to the ODOT record in order to retain it. ODFW is noted as the data source for those fields (fpbFPasONm). The Oregon Department of Transportation PONTIS data were exported in March 2015 into a replica copy of the enterprise geodatabase and posted to the OFPBDS enterprise geodatabase. Specific notes regarding the PONTIS bridge and culvert data: * The coordinate system of the spatial coordinates in the fpbLong and fpbLat fields is GCS_North_American_1983. * A bridge is defined as a structure having an opening measured along the center of the path of more than 20 feet. Bridges include culverts on the state highway system that have an opening of as little as 6 feet. For city and county bridges, all structures with an opening of 20 feet are included. Some cities and counties provided information on structures with an opening of less than 20 feet. *Because ODOT does not collect information on fish passage status, where there was a definitive match between an ODOT record and an OFPBDS feature with fish passage barrier status, that attribute information was merged from the OFPBDS record to the ODOT record in order to retain it. ODFW is noted as the data source for those fields (fpbFPasONm). *Passage status for a number of bridges and culverts was undetermined at the time data were integrated. These features require additional analysis to determine their fish passage status. Consequently, they may completely or partially pass most if not all the species and life stages that have a need to migrate through the affected stream reach. *ODOT stream names are local names, and may differ significantly from GNIS names for the same location. *Where there is stream identifier (fpbStrID), and/or stream measure (fpbStrMeas) data are linear-referenced to the 1:24,000-scale PNW Framework Hydrography. 2015-03-02T00:00:00 Ruth Schellbach ODFW GIS Technician 4034 Fairview Industrial Dr Salem Oregon 97302 ruth.e.schellbach@state.or.us Ruth Schellbach Converted Oregon Department of Fish and Western Oregon Rearing Project (WORP) Barrier data into the Oregon Fish Passage Barrier Data Standard (OFPBDS) format and loaded the data into the OFPBDS geodatabase. The ODFW WORP data exists in two Excel spreadsheets, covering surveyed sites from 1998 to 2009, and 2010 to 2014. A conversion outline, or crosswalk, between WORP and OFPBDS attributes and attribute values was developed. Western Oregon Rearing Project staff who compiled the data was consulted regarding the crosswalk. OFPBDS fields were then added to the WORP records and attribute values for all barrier features were populated in the OFPBDS fields. WORP data was then analyzed for duplication with OFPBDS records. Where Western Oregon Rearing Project fish barrier features were duplicates of OFPBDS features, missing attribute information was transferred to OFPDBS records. Spatial proximity along with attribute similarity was used to identify potential duplicates. The threshold distance default was 200 feet. Points greater than 200 feet from a current OFPBDS feature location were considered new features and added. Features within 200 feet of OFPBDS features were considered potential duplicates, based on spatial proximity. Features which were potential duplicates due to proximity were compared by key attributes: stream name, road name, feature type, and specifics. If there was still a question regarding duplication after this comparison, the feature was put aside in a separate feature class for consultation. The WORP data were exported in June 2015 into a replica copy of the enterprise geodatabase and posted to the OFPBDS enterprise geodatabase. Specific notes regarding the Western Oregon Rearing Project fish passage barrier data: * The coordinate system of the spatial coordinates in the fpbLong and fpbLat fields is GCS_North_American_1983. * The WORP surveys note and locate barrier features at the time of fish surveys. Fish Passage Status for WORP barrier features was considered totally blocking, unless notes indicated otherwise. ODFW staff used gradient, pool presence, drop/height, and other biologists’ notes to determine passage status other than “Blocked”. *Where there is stream identifier (fpbStrID), and/or stream measure (fpbStrMeas) data are linear-referenced to the 1:24,000-scale PNW Framework Hydrography. 2015-06-01T00:00:00 Ruth Schellbach ODFW GIS Technician 4034 Fairview Industrial Dr Salem Oregon 97302 ruth.e.schellbach@state.or.us Transferred BLM removed and replaced culvert data into the Oregon Fish Passage Barrier Data Standard (OFPBDS) format and loaded the data into the OFPBDS geodatabase. BLM removed and replaced culvert data exists in a Microsoft Excel spreadsheet. A conversion outline, or crosswalk, between the BLM data and OFPBDS attributes and attribute values was developed. BLM staff was consulted regarding the crosswalk. OFPBDS fields were then added to the BLM records and attribute values for all culvert features were populated in the OFPBDS fields. BLM culvert data was then analyzed for duplication with OFPBDS records. Spatial proximity along with attribute similarity was used to identify potential duplicate locations. The threshold distance default was 150 meters. Points greater than 150 meters from a current OFPBDS feature location were considered new features and added to OFPBDS. Features within 150 meters of OFPBDS features were considered a potential duplicate location, or replacements for older culverts, based on spatial proximity. Features which were potential duplicates due to proximity were compared by key attributes: stream name, road name, and BLM plans. If there was still a question regarding duplication after this comparison, the feature was put aside in a separate feature class for consultation. Where BLM features were located in proximity to an OFPBDS feature, the OFPBDS feature was updated if removed or modified, and the BLM feature was added as the replacement feature in OFPBDS. The BLM removed and replaced culvert data were exported in June 2015 into a replica copy of the enterprise geodatabase and posted to the OFPBDS enterprise geodatabase. Specific notes regarding the BLM data: * The coordinate system of the spatial coordinates in the fpbLong and fpbLat fields is GCS_North_American_1983. *Passage status for new features was considered “Completely Passable” by evaluation of design. * Where there is stream identifier (fpbStrID), and/or stream measure (fpbStrMeas) data are linear-referenced to the 1:24,000-scale PNW Framework Hydrography. 2015-06-01T00:00:00 Ruth Schellbach ODFW GIS Technician 4034 Fairview Industrial Dr Salem Oregon 97302 ruth.e.schellbach@state.or.us Ruth Schellbach Transferred U.S. Forest Service fish passage barrier data into the Oregon Fish Passage Barrier Data Standard (OFPBDS) format and loaded the data into the OFPBDS geodatabase. USFS fish passage barrier data exists in an ArcGIS file geodatabase and a personal geodatabase (May 2015). A conversion outline, or crosswalk, between the USFS data and OFPBDS attributes and attribute values was developed. USFS staff was consulted regarding the crosswalk. OFPBDS fields were then added to the USFS records and attribute values for all features were populated in the OFPBDS fields. USFS data was then analyzed for duplication with OFPBDS records. Spatial proximity along with attribute similarity was used to identify potential duplicate locations. The threshold distance default was 150 meters. Points greater than 150 meters from a current OFPBDS feature location were considered new features and added to OFPBDS. Features within 150 meters of OFPBDS features were considered a potential duplicate location, or replacements for older culverts, based on spatial proximity. Features which were potential duplicates due to proximity were compared by key attributes: stream name, road name, barrier specifics. If there was still a question regarding duplication after this comparison, the feature was put aside in a separate feature class for consultation. Where USFS data features were located in proximity to an existing OFPBDS feature, the OFPBDS feature was updated if removed or modified, or attribute information was missing, and a new USFS feature was added if there was a replacement feature for the original OFPBDS feature. The USFS data were exported in July 2015 into a replica copy of the enterprise geodatabase and posted to the OFPBDS enterprise geodatabase. Specific notes regarding the USFS data: * The coordinate system of the spatial coordinates in the fpbLong and fpbLat fields is GCS_North_American_1983. *USFS Passage status “RED” was attributed as “Partially passable” in OFPBDS, as it does not distinguished between “Not passable” for any species at any time, and “Partially passable” per the OFPBDS standard. Some features attributed as “Partially passable” may in fact be totally blocking to fish passage. *Passage status for features that replaced existing culverts was considered “Completely Passable” by evaluation of design. 2015-07-01T00:00:00 Ruth Schellbach ODFW GIS Technician 4034 Fairview Industrial Dr Salem Oregon 97302 ruth.e.schellbach@state.or.us Ruth Schellbach Ruth Schellbach The OFPBDS were reviewed for inconsistencies and in-accuracies based business rules and field rules outline in the OFPBDS data standard document (http://www.oregon.gov/DAS/CIO/GEO/docs/bioscience/oregonfishpassagebarrierdatastandardv1dot1.pdf). Focus was on Quality Control (QC) for 20 required fields, or minimum non-graphic data elements, however, QC analysis was also completed on the 43 other non-required fields. The general framework for the QC process included defining potential errors, searching for, identifying, and documenting errors, and correcting errors. When any error correction was made, the fpbRevDt was updated to reflect the date the update was made. A frequency analysis was completed using the Summary Statistics Tool “Count” for the 20 required fields, and for 43 non-required fields. This analysis resulted in counts for fields which were used to identify null values that need to be populated with “Null”, records that are using the same name slightly differently (for example: Oregon Department of Fish and Wildlife vs. ODFW) or misspellings, fields that were duplicated due to capitalization inconsistencies, date inconsistencies, and missing required fields. All records were reviewed for relevancy (for example, the date 18050710 is not accurate, since data was not collected in the year 1810). Evaluation was done across records where business rules identified that if one record was defined a certain way, than another record should be defined accordingly. This was completed for Feature Type and Feature Name pair, and Passage Status and Evaluation Method pair. The select by attribute tool was used to query errors, and field calculator was used to update selected records. There were 3,369 records updated to remove errors or inconsistencies (only for required fields). Other non-required field errors still need to be updated in the OFPBDS. Details on the QC processes are available here: Fish\Fish Share\GIS\FishPassageBarrierInventory\QA\Documentation\ FPBData_QA_Steps_Final.xlsx. Locations of points in the OFPBDS feature class were evaluated. Actual locations of points in the feature class were calculated by adding two new fields to a copy of the versioned OFPBDS database, and using the “calculate geometry” tool. These were then compared with the coordinates hosted in the attribute fields fpbLong & fpbLat. 1,272 points had locations in the feature class that were different from the recorded locations in the attribute table. Calculate geometry was used to update these fields so their attributes accurately reflect their location. OFPBDS data were evaluated for potential duplicates and for potential removal from the database throughout the process, and through targeted QC processes. There were 868 records within 30 meters of each other that were identified as potential duplicates and were evaluated by comparing by key attributes: data originator, stream name, road name, and barrier specifics. A new field created, and features were reviewed and classified as “Not Duplicate,” “Maybe Duplicate,” and “Yes Duplicate.” Currently, 25% of the records have been reviewed and given a duplicate classification. Records were also evaluated by barrier size (width), and compared with stream size (ODF fish presence data); there were 218 small barriers (<= 5 feet width) that exist on large (OFS classicifaction) rivers. These features were put aside in a separate geodatabase, by feature classes by basin, for review as potential barriers for NHD linear referencing review. This geodatabase is available here: Fish\Fish Share\GIS\FishPassageBarrierInventory\QA\Working\QA_GDBs\fpbSmall_LargeRiver.gdb. 2015-07-31T00:00:00 Kate Sherman ODFW GIS Technician 4034 Fairview Industrial Dr Salem Oregon 97302 kate.j.sherman@state.or.us Linear Referenced data in the Oregon Department of Fish and Wildlife Fish Passage Barrier Data (OFPBD) to the National Hydrography Dataset (NHD). After new data are added to the OFPBDS, their attributes lack data on the barrier’s relationship to the NHD. The last effort to linear reference records was completed in xxxx, and since then, new data were added to the OFBPDS. There were more than 10,000 records that had did not have NHD values. These points were selected, and a new feature class of these records created for processing and linear referencing to NHD. These points were further subdivided by Hydrological Unit Code (HUC) 4 boundary area (see table 1) for faster data processing. Using Hydro Event Management (HEM) Tools in ArcGIS 10.2.2, linear referencing was completed for OFPBD points using NHD Flowine Data, following standardized methods (Appendix F: FishPassageBarrierInventory\Data_Management_Plan\AppendixF). A search tolerance of 10 meters was chosen for processing to try and limit the number of barriers that get inaccurately linear referenced. A total of 10,652 points were processed, of which 5,824 (55%) successfully linear referenced to NHD (see results by HUC in Table 2). 2015-08-03T00:00:00 Kate Sherman ODFW GIS Technician 4034 Fairview Industrial Dr Salem Oregon 97302 kate.j.sherman@state.or.us Kate Sherman Extracted fish passage barrier data from the Oregon Department of Fish and Wildlife Aquatic Inventory Project (AIP) habitat unit data and transferred it into the Oregon Fish Passage Barrier Data Standard (OFPBDS) format and loaded into the OFPBDS geodatabase. AIP fish passage barrier data exists online in shapefile (shp) format. The last data from Aquatic Inventories was extracted and transferred into the OFPBDS in 2010, and included data collected as part of the AQI through part of 2009. Data collected from 2009-2014 was downloaded from the AQI website and compiled into a geodatabase and cross-referenced against data transferred in 2010 to make sure no duplicate datasets were downloaded. Models were used to extract fish passage barrier information from the AIP data. A data crosswalk, developed in 2010, was used to derive barrier feature points for the OFPBDS from the AIP habitat unit data. OFPBDS fields were then added to the AIP Habitat Unit barrier feature tables and attribute values were populated in the OFPBDS fields. AIP habitat unit barrier data were then analyzed for duplication with OFPBDS records. Spatial proximity along with attribute similarity was used to identify potential duplicate locations. The threshold distance default was 150 meters. Points greater than 150 meters from a current OFPBDS feature location were considered new features and added to OFPBDS. Features within 150 meters of OFPBDS features were considered a potential duplicate location, or replacements for older culverts, based on spatial proximity. Features which were potential duplicates due to proximity were compared by key attributes: stream name, road name, barrier specifics. If there was still a question regarding duplication after this comparison, the feature was put aside in a separate feature class for consultation. Where AIP habitat data features were located in proximity to an existing OFPBDS feature, the OFPBDS feature was modified if attribute information was missing, and a new AIP habitat feature was added if there was a replacement feature for the original OFPBDS feature. The data were exported in August 2015 into a versioned copy of the enterprise OFPBDS geodatabase and posted in the OFPBDS enterprise geodatabase. A total of 64 new barriers were added to the OFPBDS. Special notes regarding AIP data: *Due to funding, only AIP datasets with the Columbia basin were processed (this included Middle Columbia, Lower Columbia, and Willamette HUC 4 level basins. * The coordinate system of the spatial coordinates in the fpbLong and fpbLat fields is NAD 1983 Lambert Conformal Conic. * The AIP Habitat Unit feature class is attributed line features for surveyed watercourses within the state. The geodatabase table contains a Unit Type field that identifies culvert crossings, artificial step structures and natural bedrock step features, i.e. waterfalls, along with a unique identifier field (HABUNT). To derive point barrier features, ODFW selected records with a Unit Type field value equal to these unit types [culvert crossings, steps created by structures, natural bedrock steps greater than 2 meters]. The Comment Code and Note fields also identified features such as dams, fish ladders and road fords. Points were generated from the selected record lines with the Feature Vertices to Points script/toolbox for line segments, using the start point of the line. Line attributes transferred to the point. *Fish passage status evaluations are based on coarse passage criteria relative to the feature type. For culverts, a drop or perch height over 0.5 feet = Partial; if the drop is equal to or greater than one foot, then a two foot or greater unit depth is needed immediately downstream (jump pool). If the downstream unit depth is equal to or greater than two feet, then the Fish Passage Status remains as “Partial”. If the downstream unit depth is less than two feet, the Fish Passage Status = Blocked. If the slope of a culvert > 5% = Partial; if the drop > 3.2 feet = Blocked . For dams and other artificial step structures – if the Height > 0.5 foot = Partial; Height > 6.6 feet = Blocked; If the height is equal to or greater than one foot, then a two foot or greater unit depth is needed immediately downstream (jump pool). If the downstream unit depth is equal to or greater than two feet, then the Fish Passage Status remains as “Partial”. If the downstream unit depth is less than two feet, the Fish Passage Status = Blocked. For natural features if the height is over 16 feet = Blocked. If the height is less than 16 feet = Unknown; if the slope is greater than or equal to 16 % over a distance of 200 meters = Blocked. Passage status for some barriers is unknown at this time. Consequently, some of these barriers may be completely passable to most if not all the species and life stages that have a need to migrate through the affected stream reach. * Project survey dates range from 2009 to 2014. Where data was seasonal, winter data was not used. * AIP Habitat Unit data exists on hydrographic line work generally at a scale of 1:100,000. Where there is a stream identifier (fpbStrID), and/or stream measure (fpbStrMeas) data are linear-referenced to the 1:24,000-scale PNW Framework Hydrography AIP Habitat Unit data is available online: http://oregonstate.edu/dept/ODFW/freshwater/inventory/habitgis.html 2015-08-03T00:00:00 Kate Sherman ODFW GIS Technician 4034 Fairview Industrial Dr Salem Oregon 97302 kate.j.sherman@state.or.us Kate Sherman Fish passage barrier identification, location and passage status were updated during an internal ODFW fish habitat distribution and barrier data review in September and October 2016. Data were derived from ODFW district files and professional opinion of district fish biologists. To improve upon the currency and comprehensiveness of Oregon's Fish Passage Barrier Data. 2016-10-18T00:00:00 Jon Bowers Oregon Dept. of Fish and Wildlife GIS Coordinator Jon Bowers 4034 Fairview Industrial Dr SE Salem Oregon 97302 jon.k.bowers@state.or.us 503-947-6097 Jon Bowers Fish passage barrier identification, location and passage status were updated during an internal ODFW review in 2018 and 2019 related to the update of the statewide Priority Fish Passage Barrier List. Data were derived from ODFW district files, OWEB, field visits and professional opinion of district fish biologists. To improve upon the currency and comprehensiveness of Oregon's Fish Passage Barrier Data. 2019-09-19T00:00:00 Kregg Smith ODFW Asst. Fish Passage Coordinator 4034 Fairview Industrial Dr SE Salem Oregon 97302 Kregg.M.Smith@state.or.us US 503-947-6217 BLM staff analyzed fish passage barrier records to determine whether they occur on BLM roads or reciprocal right of way roads. Adjustments were made to the Originator Name field for records that came to the database from sources other than the BLM, but where the BLM should have some stewardship responsibility. Also, barrier owner information was updated based on an analysis with the current land management dataset. To improve upon the currency and comprehensiveness of Oregon's Fish Passage Barrier Data. 2019-09-27T00:00:00 Jon Bowers Oregon Dept. of Fish and Wildlife GIS Coordinator Jon Bowers 4034 Fairview Industrial Dr SE Salem Oregon 97302 jon.k.bowers@state.or.us 503-947-6097 Jon Bowers The Oregon Fish Passage Barrier Data Standard (OFPBDS) database is not a comprehensive representation of fish passage barriers in Oregon. The OFPBDS contains barrier features from approximately 19 agencies / organizations that are listed in the abstract. The OFPBDS database may not contain all the barrier records from any one agency. Existing fish passage barrier data from most agencies / organizations in Oregon have been incorporated into the OFPBDS database. Data from the US Forest Service, Clackamas county and likely other sources will be incorporated into a future version of the dataset. Though the intent is to make the OFPBDS database comprehensive, current and accurate, the dataset remains a work in progress. Barrier features in the Oregon Fish Passage Barrier Data Standard (OFPBDS) dataset contain the attributes which were provided by the data originators. When barrier data are converted into the OFPBDS format, attributes for certain fields (e.g. fish passage status - fpbFPasSta) become standardized. Among the source datasets, there is wide variation in the number and type of attributes, including those that relate to OFPBDS fields. Attribute values for particular fields are not always consistent among the originators. Many barrier records may contain information which does not reflect existing barrier conditions because feature conditions have changed since the last assessment or because more recent information has not yet been incorporated into the database. Many of the source datasets contain records collected years ago or records which are considered temporary (such as those ODOT features with a fpbOFtrID value beginning with "T"). Some features contain current and accurate attribution and others may not. In cases where attributes have been populated through automated data processing routines (e.g. linear referencing), quality assurance measures have been taken to identify and correct inaccurate assignement of attribute values. In order to improve the quality of the OFPBDS dataset over the coming months and years, field verification of fish passage barriers will be essential for improving the currency, completeness and accuracy of the data. Locational accuracy of barrier features varies. The fpbLocAccu attribute provides a measure for positional accuracy for a given record. 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