Forest Stewardship Analysis Project - Pilot Overlay Study Methodology for the State of Rhode Island Outline • Project Summary • Factors of Influence and Data layer development • The Overlay Model Project Summary The State of RI conducted a simple non-weighted additive model for 11 of the 12 layers suggested as input for The Spatial Analysis Project (SAP). Because the model was unweighted and because RI is such a small state, it was agreed that patch size was unimportant. The RI Division of Forest Environment sees opportunity for Stewardship on relatively small forest plots that might have been overlooked had we considered patch size as an analysis factor. The SAP will prove useful not only to the State Foresty Program, but also in ongoing work in land conservation and habitat protection via the State Division of Fish & Wildlife. Factors of Influence and Data layer development Fire Protection Assessment: The only available fire assessment data came from the NorthEast Compact Fire Assessment and was generously provided to us by the Maine State Forestry Program. These data characterize risk based on both resource damage and threat to life & property. Medium and high were combined to create the fire risk layer. Risk of Insects/Pests: This layer shows areas of Rhode Island that have had measured insect infestations within the last 5 years. Data provided by the USFS based on local Aerial Detection Surveys. Risk of Development (change in census block households): This layer shows areas of Rhode Island were change in households per square mile between 1990 and 2000 where the increase in the number of households has been 0 to 20. Change in this range is considered high enough to highlight the need for Stewardship, yet low enough where changes in attitude can still provide an alternative to urban sprawl. For Connecticut the Census block group data was collected and combined by the USFS. Private Forested Lands: These are forested lands not within the extent of the Analysis Mask. The forested land coverage was derived from the Rhode Island Geographic Information System (RIGIS) 1995 Anderson Level 3 Land-use/Land-cover dataset and the RIGIS 1988 Wetlands data . These data have ½ acre resolution and were considered superior to the MRLC National Land Cover Datalayer. The data are functionally equivalent to the (NLCD) for forested uplands and woody wetlands. The table below crosswalks the RIGIS data values with the MRLC/NLCD equivalents. RI-methodology.doc 3/2/2007 Page 1 of 3 Forested Land RIGIS/MRLC Crosswalk RIGIS Dataset Code LU/LC 1995 310 Deciduous Forest > 80% Hardwood LU/LC 1995 320 Evergreen Forest > 80% Hardwood LU/LC 1995 330 MixedDeciduous Forest 50 to 80% Hardwood LU/LC 1995 340 Mixed Evergreen Forest 50 to 80% Softwood Wetland 1988 FOA Forested Wetland: Coniferous Wetland 1988 FOB Forested Wetland: Deciduous MRLC 41 Deciduous Forest 42 Evergreen Forest 43 Mixed Forest 43 Mixed Forest 91 Palustrine Forested Wetland 91 Palustrine Forested Wetland Private Non-Forested Lands: Non-Forested undeveloped private lands, the counterpart to the previous layer, were taken from following RIGIS LU/LC 1995 classes: Non-Forested Land RIGIS LU/lc 1995/MRLC Crosswalk RIGIS Class MRLC/NLCD Class 210 Pasture 81 Pasture/Hay 220 Cropland 82 Cultivated Crops 230 Orchards, Groves & Nurseries 82 Cultivated Crops ? 250 Idle Agriculture 71 Grasslands/Herbaceous 400 Brushland 52 Shrub/Scrub 600 Wetland * 95 Emergent Herbaceous 96 Palustrine Emergent 750 Transitional Areas 21 Developed Open Space 760 Mixed Barren Areas 31 Barren Land *Excluding Forested Wetlands that were included in the Forested Land Layer Wetlands: 1988 ½ acre resolution statewide dataset based on Cowardin classification scheme. Forest Patches: RI did not consider forest patch size in it’s analysis because of the small size of the state and the attendant belief that good stewardship can and is occuring on small lot sizes. Riparian Corridors: 300ft Riparian buffer based on 1:24,000 RIGIS Stream Centerline and River Polygon data. Natural Heritage Priority Habitats (Threatened and Endangered Species): Estimated habitat and range of rare species and noteworthy natural communities. Proximity to Publicly Protected Lands: All publicly protected permanent conservation lands held by Federal, State or Local Government entities. RI-methodology.doc 3/2/2007 Page 2 of 3 Slopes: Slopes between 15% & 30% derived from a 1:5000 Digital Terrain Model created in 1997 for a statewide orthophotography project Public Water Supply Areas: This raster data layer is a composite derived from the following 3 CT DEP vector data layers: Wellhead Protection Areas – Zone II, Wellhead Protection Areas – Interim, and Surface Water Supply Protection Areas. The final grid is a 1/0 layer that describes areas falling into the above categories. Analysis Mask: The analysis mask represents all developed land use types including commercial, industrial, residential, developed recreation, transportation, open water, and protected public lands. Features in this layer are considered outside the areas where the private stewardship will be applied; to be removed from the full analysis. As with previous layers, the mask was based upon the RIGIS Landuse/Landcover 1995 layer. Analysis Methodology RI elected to use an unweighted analysis for this project. Previous efforts at developing a weighting scheme for openspace and natural habitat protection could find little agreement among participants on priortizing landscape characteristics. The RI Division of Forestry staff agreed that they were not comfortable in applying weighting factors to this analysis. All of the model input layers previously described were converted to a grid format using a 100-ft (10,000 ft^2) cell size. Each layer was coded as 0 or 1 indicating absence or presence of the resource. For each analysis, layers were summed vertically to determine how many co-ocurring resources were found for each 10,000 sq-ft cell. After summation the data was classified using a natural breaks grouping and then reclassified as 1,2 or 3 representing a low, medium or high value for the cell. A mask was used to exclude lands considered outside the stewardship program designation (developed land, open water, public lands). RI developed six maps according to the requirements outlined in the SAP documentation provided us. RI-methodology.doc 3/2/2007 Page 3 of 3