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: Random utility model (RUM) Valuing Recreational fishing quality in streams and rivers, Michigan, USA (EM-660)
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EM Identity and Description
EM Identification (* Note that run information is shown only where run data differ from the "parent" entry shown at left)
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EM ID
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New or revised model | New or revised model | EM-660 | New or revised model | Continuation of trends |
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EM Short Name
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Community flowering date, Central French Alps | Rate of Fire Spread | RUM: Valuing fishing quality, Michigan, USA | Recreational fishery index, USA | CommunityViz, Albany county, Wyoming |
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EM Full Name
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Community weighted mean flowering date, Central French Alps | Rate of Fire Spread | Random utility model (RUM) Valuing Recreational fishing quality in streams and rivers, Michigan, USA | Recreational fishery index for streams and rivers, USA | Wyoming Community Viz TM Partnership Phase I Pilot: Aquifer Protection and Community Viz TM in Albany County, Wyoming. |
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EM Source or Collection
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EU Biodiversity Action 5 | * | None | US EPA | * |
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EM Source Document ID
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260 | 306 |
382 ?Comment:Data collected from Michigan Recreational Angler Survey, a mail survey administered monthly to random sample of Michigan fishing license holders since July 2008. Data available taken from 2008-2010. |
414 |
479 ?Comment:Published as a report by the University of Wyoming, but no record of peer review. |
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Document Author
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Lavorel, S., Grigulis, K., Lamarque, P., Colace, M-P, Garden, D., Girel, J., Pellet, G., and Douzet, R. | Rothermel, Richard C. | Melstrom, R. T., Lupi, F., Esselman, P.C., and R. J. Stevenson | Lomnicky. G.A., Hughes, R.M., Peck, D.V., and P.L. Ringold | Lieske, S. N., Mullen, S., Knapp, M., & Hamerlinck, J. D. |
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Document Year
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2011 | 1972 | 2014 | 2021 | 2003 |
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Document Title
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Using plant functional traits to understand the landscape distribution of multiple ecosystem services | A Mathematical model for predicting fire spread in wildland fuels | Valuing recreational fishing quality at rivers and streams | Correspondence between a recreational fishery index and ecological condition for U.S.A. streams and rivers. | Wyoming Community Viz TM Partnership Phase I Pilot: Aquifer Protection and Community Viz TM in Albany County, Wyoming |
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Document Status
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* | Documented, not peer reviewed | Peer reviewed and published | * | Not peer reviewed but is published (explain in Comment) |
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Comments on Status
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* | Published USDA Forest Service report | Published journal manuscript | * | Published report |
Software and Access (* Note that run information is shown only where run data differ from the "parent" entry shown at left)
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EM ID
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New or revised model | New or revised model | EM-660 | New or revised model | Continuation of trends |
| * | http://firelab.org/project/farsite | Not applicable | * | https://communityviz.com/ | |
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Contact Name
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Sandra Lavorel | Charles McHugh | Richard Melstrom | Gregg Lomnicky | Scott Lieske |
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Contact Address
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Laboratoire d’Ecologie Alpine, UMR 5553 CNRS Université Joseph Fourier, BP 53, 38041 Grenoble Cedex 9, France | RMRS Missoula Fire Sciences Laboratory, 5775 US Highway 10 West, Missoula, MT 59808 | Department of Agricultural Economics, Oklahoma State Univ., Stillwater, Oklahoma, USA | 200 SW 35th St., Corvallis, OR, 97333 | Department of Agricultural & Applied Economics University of Wyoming, Laramie WY 82071 |
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Contact Email
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sandra.lavorel@ujf-grenoble.fr | cmchugh@fs.fed.us | melstrom@okstate.edu | lomnicky.gregg@epa.gov | lieske@uwyo.edu |
EM Description (* Note that run information is shown only where run data differ from the "parent" entry shown at left)
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EM ID
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New or revised model | New or revised model | EM-660 | New or revised model | Continuation of trends |
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Summary Description
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ABSTRACT: "Here, we propose a new approach for the analysis, mapping and understanding of multiple ES delivery in landscapes. Spatially explicit single ES models based on plant traits and abiotic characteristics are combined to identify ‘hot’ and ‘cold’ spots of multiple ES delivery, and the land use and biotic determinants of such distributions. We demonstrate the value of this trait-based approach as compared to a pure land-use approach for a pastoral landscape from the central French Alps, and highlight how it improves understanding of ecological constraints to, and opportunities for, the delivery of multiple services." AUTHOR'S DESCRIPTION: "Community-weighted mean date of flowering onset was modelled using mixed models with land use and abiotic variables as fixed effects (LU + abiotic model) and year as a random effect…and modelled for each 20 x 20 m pixel using GLM estimated effects for each land use category and estimated regression coefficients with abiotic variables." | ABSTRACT: "The development of a mathematical model for predicting rate of fire spread and intensity applicable to a wide range of wildland fuels is presented from the conceptual stage through evaluation and demonstration of results to hypothetical fuel models. The model was developed for and is now being used as a basis for appraising fire spread and intensity in the National Fire Danger Rating System. The initial work was done using fuel arrays composed of uniform size particles. Three fuel sizes were tested over a wide range of bulk densities. These were 0.026-inch-square cut excelsior, 114-inch sticks, and 112-inch sticks. The problem of mixed fuel sizes was then resolved by weighting the various particle sizes that compose actual fuel arrays by either surface area or loading, depending upon the feature of the fire being predicted. The model is complete in the sense that no prior knowledge of a fuel's burning characteristics is required. All that is necessary are inputs describing the physical and chemical makeup of the fuel and the environmental conditions in which it is expected to burn. Inputs include fuel loading, fuel depth, fuel particle surface-area-to-volume ratio, fuel particle heat content, fuel particle moisture and mineral content, and the moisture content at which extinction can be expected. Environmental inputs are mean wind velocity and slope of terrain. For heterogeneous mixtures, the fuel properties are entered for each particle size. The model as originally conceived was for dead fuels in a uniform stratum contiguous to the ground, such as litter or grass. It has been found to be useful, however, for fuels ranging from pine needle litter to heavy logging slash and for California brush fields." **FARSITE4 will no longer be supported or available for download or further supported. FlamMap6 now includes FARSITE.** | ABSTRACT: " This paper describes an economic model that links the demand for recreational stream fishing to fish biomass. Useful measures of fishing quality are often difficult to obtain. In the past, economists have linked the demand for fishing sites to species presence‐absence indicators or average self‐reported catch rates. The demand model presented here takes advantage of a unique data set of statewide biomass estimates for several popular game fish species in Michigan, including trout, bass and walleye. These data are combined with fishing trip information from a 2008–2010 survey of Michigan anglers in order to estimate a demand model. Fishing sites are defined by hydrologic unit boundaries and information on fish assemblages so that each site corresponds to the area of a small subwatershed, about 100–200 square miles in size. The random utility model choice set includes nearly all fishable streams in the state. The results indicate a significant relationship between the site choice behavior of anglers and the biomass of certain species. Anglers are more likely to visit streams in watersheds high in fish abundance, particularly for brook trout and walleye. The paper includes estimates of the economic value of several quality change and site loss scenarios. " | ABSTRACT: [Sport fishing is an important recreational and economic activity, especially in Australia, Europe and North America, and the condition of sport fish populations is a key ecological indicator of water body condition for millions of anglers and the public. Despite its importance as an ecological indicator representing the status of sport fish populations, an index for measuring this ecosystem service has not been quantified by analyzing actual fish taxa, size and abundance data across the U.S.A. Therefore, we used game fish data collected from 1,561 stream and river sites located throughout the conterminous U.S.A. combined with specific fish species and size dollar weights to calculate site-specific recreational fishery index (RFI) scores. We then regressed those scores against 38 potential site-specific environmental predictor variables, as well as site-specific fish assemblage condition (multimetric index; MMI) scores based on entire fish assemblages, to determine the factors most associated with the RFI scores. We found weak correlations between RFI and MMI scores and weak to moderate correlations with environmental variables, which varied in importance with each of 9 ecoregions. We conclude that the RFI is a useful indicator of a stream ecosystem service, which should be of greater interest to the U.S.A. public and traditional fishery management agencies than are MMIs, which tend to be more useful for ecologists, environmentalists and environmental quality agencies.] | The Wyoming Community VizTM Partnership was established in 2001 to promote the use of geographic information system-based planning support systems and related decision support technologies in community land-use planning and economic development activities in the State of Wyoming. Partnership members include several state agencies, local governments and several nongovernment organizations. Partnership coordination is provided by the Wyoming Rural Development Council. Research and technical support is coordinated by the Wyoming Geographic Information Science Center’s Spatial Decision Support System Research Program at the University of Wyoming. In June 2002, the Partnership initiated a three-phase plan to promote Community VizTM based planning support systems in Wyoming. Phase I of the Partnership plan was a “proof of concept” pilot project set in Albany County in southeastern Wyoming. The goal of the project was to demonstrate the application of Community VizTM to a Wyoming-specific issue (in this case, aquifer protection) and to determine potential challenges for broader adoption in terms of data requirements, computing infrastructure and technological expertise. The results of the Phase I pilot project are detailed in this report. Efforts are currently underway to secure funding for Phase II of the plan, which expands the use of Community VizTM into four additional Wyoming communities. Specific Phase II objectives are to expand the type and number of issues addressed by Community VizTM and increase the use of Community VizTM in the planning process. As a part of Phase II the Partnership will create a technical assistance network aimed at assisting communities with the technical challenges in applying the software to their planning issues. The third phase will expand the program to more communities in the state, maintain the technical assistance network, and monitor the impact of Community VizTM on the planning process. |
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Specific Policy or Decision Context Cited
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* | * | None identified | * | None provided |
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Biophysical Context
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Elevation ranges from 1552 to 2442 m, on predominantly south-facing slopes | Not applicable | stream and river reaches of Michigan | None | Groundwater recharge area, City of Laramie |
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EM Scenario Drivers
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No scenarios presented | No scenarios presented | targeted sport fish biomass | N/A | Continuation of trends |
EM Relationship to Other EMs or Applications
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EM ID
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New or revised model | New or revised model | EM-660 | New or revised model | Continuation of trends |
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Method Only, Application of Method or Model Run
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Method + Application | Method Only | Method + Application (multiple runs exist) | Method + Application | Model Run Associated with a Specific EM Application |
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New or Pre-existing EM?
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New or revised model | New or revised model | New or revised model | New or revised model | Continuation of trends |
Related EMs (for example, other versions or derivations of this EM) described in ESML
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EM ID
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New or revised model | New or revised model | EM-660 | New or revised model | Continuation of trends |
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Document ID for related EM
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Doc-260 | Doc-269 | None | None | None | Doc-473 |
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EM ID for related EM
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EM-65 | EM-66 | EM-68 | EM-69 | EM-70 | EM-79 | EM-80 | EM-81 | EM-82 | EM-83 | None | None | None | None |
EM Modeling Approach
EM Relationship to Time (* Note that run information is shown only where run data differ from the "parent" entry shown at left)
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EM ID
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New or revised model | New or revised model | EM-660 | New or revised model | Continuation of trends |
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EM Temporal Extent
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2007-2008 | Not applicable | 2008-2010 | 2013-2014 | 2050 |
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EM Time Dependence
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* | Not applicable | time-stationary | time-dependent | * |
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EM Time Reference (Future/Past)
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* | * | Not applicable | past time | * |
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EM Time Continuity
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* | * | Not applicable | discrete | * |
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EM Temporal Grain Size Value
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* | * | Not applicable | 1 | * |
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EM Temporal Grain Size Unit
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* | * | Not applicable | Year | * |
EM spatial extent (* Note that run information is shown only where run data differ from the "parent" entry shown at left)
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EM ID
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New or revised model | New or revised model | EM-660 | New or revised model | Continuation of trends |
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Bounding Type
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Physiographic or Ecological | Not applicable | Watershed/Catchment/HUC | Geopolitical | * |
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Spatial Extent Name
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Central French Alps | Not applicable | HUCS in Michigan | United States | Laramie City's aquifer protection area |
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Spatial Extent Area (Magnitude)
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10-100 km^2 | Not applicable | 100,000-1,000,000 km^2 | >1,000,000 km^2 | 10-100 km^2 |
Spatial Distribution of Computations (* Note that run information is shown only where run data differ from the "parent" entry shown at left)
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EM ID
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New or revised model | New or revised model | EM-660 | New or revised model | Continuation of trends |
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EM Spatial Distribution
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* | Not applicable | spatially distributed (in at least some cases) | * | spatially lumped (in all cases) |
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Spatial Grain Type
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area, for pixel or radial feature | Not applicable | other (specify), for irregular (e.g., stream reach, lake basin) | length, for linear feature (e.g., stream mile) | Not applicable |
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Spatial Grain Size
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20 m x 20 m | Not applicable | reach in HUC | stream reach (site) | Not applicable |
EM Structure and Computation Approach (* Note that run information is shown only where run data differ from the "parent" entry shown at left)
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EM ID
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New or revised model | New or revised model | EM-660 | New or revised model | Continuation of trends |
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EM Computational Approach
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Analytic | Analytic | Numeric | Analytic | * |
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EM Determinism
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* | * | deterministic | * | * |
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Statistical Estimation of EM
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* |
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* | * |
Model Checking Procedures Used (* Note that run information is shown only where run data differ from the "parent" entry shown at left)
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EM ID
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New or revised model | New or revised model | EM-660 | New or revised model | Continuation of trends |
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Model Calibration Reported?
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* | Not applicable | No | * | Unclear |
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Model Goodness of Fit Reported?
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* | Not applicable | Yes | No | No |
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Goodness of Fit (metric| value | unit)
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* |
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* | * |
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Model Operational Validation Reported?
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* | * | No | * | Unclear |
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Model Uncertainty Analysis Reported?
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* | Not applicable | No | * | Unclear |
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Model Sensitivity Analysis Reported?
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* | Not applicable | No | * | Unclear |
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Model Sensitivity Analysis Include Interactions?
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* | * | Not applicable | * | * |
EM Locations, Environments, Ecology
Location of EM Application (* Note that run information is shown only where run data differ from the "parent" entry shown at left)
Terrestrial location (Classification hierarchy: Continent > Country > U.S. State [United States only])
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| New or revised model | New or revised model | EM-660 | New or revised model | Continuation of trends |
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* |
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Marine location (Classification hierarchy: Realm > Region > Province > Ecoregion)
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| New or revised model | New or revised model | EM-660 | New or revised model | Continuation of trends |
| * | * | None | * | * |
Centroid Lat/Long (Decimal Degree)
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EM ID
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New or revised model | New or revised model | EM-660 | New or revised model | Continuation of trends |
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Centroid Latitude
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45.05 | -9999 | 45.12 | 36.21 | 41.31 |
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Centroid Longitude
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6.4 | -9999 | 85.18 | -113.76 | -105.46 |
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Centroid Datum
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* | Not applicable | WGS84 | * | * |
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Centroid Coordinates Status
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Provided | Not applicable | Estimated | * | * |
Environments and Scales Modeled (* Note that run information is shown only where run data differ from the "parent" entry shown at left)
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EM ID
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New or revised model | New or revised model | EM-660 | New or revised model | Continuation of trends |
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EM Environmental Sub-Class
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Agroecosystems | Grasslands | Terrestrial Environment (sub-classes not fully specified) | Rivers and Streams | * | Ground Water | Terrestrial Environment (sub-classes not fully specified) |
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Specific Environment Type
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Subalpine terraces, grasslands, and meadows. | Not applicable | stream reaches | reach | watershed |
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EM Ecological Scale
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Not applicable | * | Ecological scale is finer than that of the Environmental Sub-class | * | Ecological scale corresponds to the Environmental Sub-class |
Organisms modeled (* Note that run information is shown only where run data differ from the "parent" entry shown at left)
Scale of differentiation of organisms modeled
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EM ID
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New or revised model | New or revised model | EM-660 | New or revised model | Continuation of trends |
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EM Organismal Scale
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Community | * | Not applicable | Guild or Assemblage | * |
Taxonomic level and name of organisms or groups identified
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| New or revised model | New or revised model | EM-660 | New or revised model | Continuation of trends |
| * | * |
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* | * |
EnviroAtlas URL
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| New or revised model | New or revised model | EM-660 | New or revised model | Continuation of trends |
| None Available | Average Annual Precipitation | The National Hydrography Dataset (NHD), The Watershed Boundary Dataset (WBD), Enabling Conditions, Employment Rate | None Available | Dasymetric Allocation of Population, Total Annual Reduced Nitrogen Deposition, Employment Rate |
EM Ecosystem Goods and Services (EGS) potentially modeled, by classification system
* Note that run information is shown only where run data differ from the "parent" entry shown at left
CICES v 4.3 - Common International Classification of Ecosystem Services (Section > Division > Group > Class)
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| New or revised model | New or revised model | EM-660 | New or revised model | Continuation of trends |
| * | * |
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(Environmental Subclass > Ecological End-Product (EEP) > EEP Subclass > EEP Modifier)
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| New or revised model | New or revised model | EM-660 | New or revised model | Continuation of trends |
| * | * |
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EM Variable Names (and Units)
* Note that for runs, variable name is displayed only where data for that variable differed by run AND those differences were reported in the source document. Where differences occurred but were not reported, the variable is not listed. Click on variable name to view details.
Predictor
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Intermediate
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EM ID
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New or revised model | New or revised model | EM-660 | New or revised model | Continuation of trends |
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Intermediate (Computed) Variables (and Units)
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None |
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* |
Response
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EM ID
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New or revised model | New or revised model | EM-660 | New or revised model | Continuation of trends |
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Observed Response Variables (and Units)
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None | None | None | * | |
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Computed Response Variables (and Units)
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