EcoService Models Library (ESML)
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Variables Details
: (EM-820)
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EM-820 | |
Document Author
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Stoddard, J.L., Herlihy, A.T., Peck, D.V., Hughes, R.M., Whittier, T.R., and E. Tarquinio |
Document Year
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2008 |
Metric range ?Comment:The range is the distribution of metric values across all of the available data. The goal is to eliminate metrics that have very small ranges (e.g., richness metrics based on only a few taxa) or that have similar values at most sites (e.g., most sites have values ¼ 0). A small range could indicate that a metric might not vary sufficiently across sites to discriminate among sites in different conditions. |
Natural gradient adjustment | Redundancy check |
Reproducibility (Signal/Noise) ?Comment:S/N= Signal to Noise The use of metrics that have relatively stable values at individual sites helps ensure that between-site differences in individual samples are caused by differences in stream condition rather than by sampling variation within a site. Sampling variation is estimated from repeat visits to individual sites. Available measures of sampling variation reflect several sources of variability (i.e., short-term indexperiod temporal variability, spatial variability within the reach, and laboratory variability). Low sampling variation is necessary if a metric is to have a highprobability of discriminating between sites in good and poor condition, and sampling variation should be small relative to the size of the among-site differences to be discriminated. We quantify metric reproducibility with a variant of the signal:noise ratio (S/N). S/N is the ratio of the variance among all sites (signal) to the variance of repeated visits to the same site (noise) (Kaufmann et al. 1999). Metrics with high S/N values are more likely to show consistent responses to stressors than are metrics with low S/N values. A metric that is perfectly correlated with a hypothetical stressor and that has no sampling variability will have an R2 ¼ 1.0 for that stressor. As S/N decreases, the maximum possible R2 value of the regression decreases because the sampling variability of the metric increases. When S/N ¼ 1, a perfect correlation between the metric and the stressor would produce R2 ¼ 0.5 (Fig. 2). We have no fixed threshold below which we eliminate metrics based on S/N. However, S/N values 1 indicate that visiting a single site twice yields as much metric variability as visiting 2 different sites. |
Responsiveness ?Comment:The ultimate test of the effectiveness of a metric is its ability to distinguish degraded from relatively undisturbed streams. A more general approach is to base the evaluation of responsiveness on the ability of a metric to distinguish least-disturbed (reference) from most-disturbed sites. |
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Variable ID
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19348 | 19351 | 19353 | 19349 | 19352 |
Not reported | Not reported | Not reported | Not reported | Not reported | |
Qualitative-Quantitative
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Quantitative (Cardinal Only) | Quantitative (Cardinal Only) | Quantitative (Cardinal Only) | Quantitative (Cardinal Only) | Quantitative (Cardinal Only) |
Cardinal-Ordinal
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Cardinal | Cardinal | Cardinal | Cardinal | Cardinal |
variable | variable | variable | unitless | variable |
Metric range ?Comment:The range is the distribution of metric values across all of the available data. The goal is to eliminate metrics that have very small ranges (e.g., richness metrics based on only a few taxa) or that have similar values at most sites (e.g., most sites have values ¼ 0). A small range could indicate that a metric might not vary sufficiently across sites to discriminate among sites in different conditions. |
Natural gradient adjustment | Redundancy check |
Reproducibility (Signal/Noise) ?Comment:S/N= Signal to Noise The use of metrics that have relatively stable values at individual sites helps ensure that between-site differences in individual samples are caused by differences in stream condition rather than by sampling variation within a site. Sampling variation is estimated from repeat visits to individual sites. Available measures of sampling variation reflect several sources of variability (i.e., short-term indexperiod temporal variability, spatial variability within the reach, and laboratory variability). Low sampling variation is necessary if a metric is to have a highprobability of discriminating between sites in good and poor condition, and sampling variation should be small relative to the size of the among-site differences to be discriminated. We quantify metric reproducibility with a variant of the signal:noise ratio (S/N). S/N is the ratio of the variance among all sites (signal) to the variance of repeated visits to the same site (noise) (Kaufmann et al. 1999). Metrics with high S/N values are more likely to show consistent responses to stressors than are metrics with low S/N values. A metric that is perfectly correlated with a hypothetical stressor and that has no sampling variability will have an R2 ¼ 1.0 for that stressor. As S/N decreases, the maximum possible R2 value of the regression decreases because the sampling variability of the metric increases. When S/N ¼ 1, a perfect correlation between the metric and the stressor would produce R2 ¼ 0.5 (Fig. 2). We have no fixed threshold below which we eliminate metrics based on S/N. However, S/N values 1 indicate that visiting a single site twice yields as much metric variability as visiting 2 different sites. |
Responsiveness ?Comment:The ultimate test of the effectiveness of a metric is its ability to distinguish degraded from relatively undisturbed streams. A more general approach is to base the evaluation of responsiveness on the ability of a metric to distinguish least-disturbed (reference) from most-disturbed sites. |
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Predictor-Intermediate-Response
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Intermediate (Computed) Variable |
Intermediate (Computed) Variable |
Intermediate (Computed) Variable |
Intermediate (Computed) Variable |
Intermediate (Computed) Variable |
Predictor Variable Type
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Not applicable | Not applicable | Not applicable | Not applicable | Not applicable |
Response Variable Type
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Not applicable | Not applicable | Not applicable | Not applicable | Not applicable |
Data Source/Type
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Not applicable | Not applicable | Not applicable | Not applicable | Not applicable |
Variable Classification Hierarchy
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5. Ecosystem Attributes and Potential Supply of Ecosystem Goods and Services |
5. Ecosystem Attributes and Potential Supply of Ecosystem Goods and Services |
5. Ecosystem Attributes and Potential Supply of Ecosystem Goods and Services |
5. Ecosystem Attributes and Potential Supply of Ecosystem Goods and Services |
5. Ecosystem Attributes and Potential Supply of Ecosystem Goods and Services |
--Biological characteristics, processes or requirements of living ecosystem components |
--Physical/chemical characteristics of nonliving ecosystem components |
--Biological characteristics, processes or requirements of living ecosystem components |
--Other, multiple, unspecified or unclear |
--Biological characteristics, processes or requirements of living ecosystem components |
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----Biological characteristics, processes or requirements of fauna |
----Other, multiple, unspecified or unclear |
----Biological characteristics, processes or requirements of fauna |
----Biological characteristics, processes or requirements of fauna |
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------Other, multiple, unspecified or unclear |
------Other, multiple, unspecified or unclear |
------Other, multiple, unspecified or unclear |
Metric range ?Comment:The range is the distribution of metric values across all of the available data. The goal is to eliminate metrics that have very small ranges (e.g., richness metrics based on only a few taxa) or that have similar values at most sites (e.g., most sites have values ¼ 0). A small range could indicate that a metric might not vary sufficiently across sites to discriminate among sites in different conditions. |
Natural gradient adjustment | Redundancy check |
Reproducibility (Signal/Noise) ?Comment:S/N= Signal to Noise The use of metrics that have relatively stable values at individual sites helps ensure that between-site differences in individual samples are caused by differences in stream condition rather than by sampling variation within a site. Sampling variation is estimated from repeat visits to individual sites. Available measures of sampling variation reflect several sources of variability (i.e., short-term indexperiod temporal variability, spatial variability within the reach, and laboratory variability). Low sampling variation is necessary if a metric is to have a highprobability of discriminating between sites in good and poor condition, and sampling variation should be small relative to the size of the among-site differences to be discriminated. We quantify metric reproducibility with a variant of the signal:noise ratio (S/N). S/N is the ratio of the variance among all sites (signal) to the variance of repeated visits to the same site (noise) (Kaufmann et al. 1999). Metrics with high S/N values are more likely to show consistent responses to stressors than are metrics with low S/N values. A metric that is perfectly correlated with a hypothetical stressor and that has no sampling variability will have an R2 ¼ 1.0 for that stressor. As S/N decreases, the maximum possible R2 value of the regression decreases because the sampling variability of the metric increases. When S/N ¼ 1, a perfect correlation between the metric and the stressor would produce R2 ¼ 0.5 (Fig. 2). We have no fixed threshold below which we eliminate metrics based on S/N. However, S/N values 1 indicate that visiting a single site twice yields as much metric variability as visiting 2 different sites. |
Responsiveness ?Comment:The ultimate test of the effectiveness of a metric is its ability to distinguish degraded from relatively undisturbed streams. A more general approach is to base the evaluation of responsiveness on the ability of a metric to distinguish least-disturbed (reference) from most-disturbed sites. |
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Spatial Extent Area
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Not applicable | Not applicable | Not applicable | Not applicable | Not applicable |
Spatially Distributed?
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No | No | No | No | No |
Observations Spatially Patterned?
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Not applicable | Not applicable | Not applicable | Not applicable | Not applicable |
Spatial Grain Type
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Not applicable | Not applicable | Not applicable | Not applicable | Not applicable |
Spatial Grain Size
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Not applicable | Not applicable | Not applicable | Not applicable | Not applicable |
Spatial Density
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Not applicable | Not applicable | Not applicable | Not applicable | Not applicable |
EnviroAtlas URL
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Metric range ?Comment:The range is the distribution of metric values across all of the available data. The goal is to eliminate metrics that have very small ranges (e.g., richness metrics based on only a few taxa) or that have similar values at most sites (e.g., most sites have values ¼ 0). A small range could indicate that a metric might not vary sufficiently across sites to discriminate among sites in different conditions. |
Natural gradient adjustment | Redundancy check |
Reproducibility (Signal/Noise) ?Comment:S/N= Signal to Noise The use of metrics that have relatively stable values at individual sites helps ensure that between-site differences in individual samples are caused by differences in stream condition rather than by sampling variation within a site. Sampling variation is estimated from repeat visits to individual sites. Available measures of sampling variation reflect several sources of variability (i.e., short-term indexperiod temporal variability, spatial variability within the reach, and laboratory variability). Low sampling variation is necessary if a metric is to have a highprobability of discriminating between sites in good and poor condition, and sampling variation should be small relative to the size of the among-site differences to be discriminated. We quantify metric reproducibility with a variant of the signal:noise ratio (S/N). S/N is the ratio of the variance among all sites (signal) to the variance of repeated visits to the same site (noise) (Kaufmann et al. 1999). Metrics with high S/N values are more likely to show consistent responses to stressors than are metrics with low S/N values. A metric that is perfectly correlated with a hypothetical stressor and that has no sampling variability will have an R2 ¼ 1.0 for that stressor. As S/N decreases, the maximum possible R2 value of the regression decreases because the sampling variability of the metric increases. When S/N ¼ 1, a perfect correlation between the metric and the stressor would produce R2 ¼ 0.5 (Fig. 2). We have no fixed threshold below which we eliminate metrics based on S/N. However, S/N values 1 indicate that visiting a single site twice yields as much metric variability as visiting 2 different sites. |
Responsiveness ?Comment:The ultimate test of the effectiveness of a metric is its ability to distinguish degraded from relatively undisturbed streams. A more general approach is to base the evaluation of responsiveness on the ability of a metric to distinguish least-disturbed (reference) from most-disturbed sites. |
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Temporal Extent
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Not applicable | Not applicable | Not applicable | Not applicable | Not applicable |
Temporally Distributed?
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Yes | No | No | Yes | Not applicable |
Regular Temporal Grain?
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Not applicable | Not applicable | Not applicable | Not applicable | Not applicable |
Temporal Grain Size Value
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Not applicable | Not applicable | Not applicable | Not applicable | Not applicable |
Temporal Grain Size Units
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Not applicable | Not applicable | Not applicable | Not applicable | Not applicable |
Temporal Density
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Not applicable | Not applicable | Not applicable | Not applicable | Not applicable |
Metric range ?Comment:The range is the distribution of metric values across all of the available data. The goal is to eliminate metrics that have very small ranges (e.g., richness metrics based on only a few taxa) or that have similar values at most sites (e.g., most sites have values ¼ 0). A small range could indicate that a metric might not vary sufficiently across sites to discriminate among sites in different conditions. |
Natural gradient adjustment | Redundancy check |
Reproducibility (Signal/Noise) ?Comment:S/N= Signal to Noise The use of metrics that have relatively stable values at individual sites helps ensure that between-site differences in individual samples are caused by differences in stream condition rather than by sampling variation within a site. Sampling variation is estimated from repeat visits to individual sites. Available measures of sampling variation reflect several sources of variability (i.e., short-term indexperiod temporal variability, spatial variability within the reach, and laboratory variability). Low sampling variation is necessary if a metric is to have a highprobability of discriminating between sites in good and poor condition, and sampling variation should be small relative to the size of the among-site differences to be discriminated. We quantify metric reproducibility with a variant of the signal:noise ratio (S/N). S/N is the ratio of the variance among all sites (signal) to the variance of repeated visits to the same site (noise) (Kaufmann et al. 1999). Metrics with high S/N values are more likely to show consistent responses to stressors than are metrics with low S/N values. A metric that is perfectly correlated with a hypothetical stressor and that has no sampling variability will have an R2 ¼ 1.0 for that stressor. As S/N decreases, the maximum possible R2 value of the regression decreases because the sampling variability of the metric increases. When S/N ¼ 1, a perfect correlation between the metric and the stressor would produce R2 ¼ 0.5 (Fig. 2). We have no fixed threshold below which we eliminate metrics based on S/N. However, S/N values 1 indicate that visiting a single site twice yields as much metric variability as visiting 2 different sites. |
Responsiveness ?Comment:The ultimate test of the effectiveness of a metric is its ability to distinguish degraded from relatively undisturbed streams. A more general approach is to base the evaluation of responsiveness on the ability of a metric to distinguish least-disturbed (reference) from most-disturbed sites. |
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Not applicable | Not applicable | Not applicable | Not applicable | Not applicable | |
Min Value
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Not applicable | Not applicable | Not applicable | Not applicable | Not applicable |
Max Value
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Not applicable | Not applicable | Not applicable | Not applicable | Not applicable |
Other Value Type
variable.detail.natureOtherEstHelp
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Not applicable | Not applicable | Not applicable | Not applicable | Not applicable |
Other Value
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Not applicable | Not applicable | Not applicable | Not applicable | Not applicable |
Metric range ?Comment:The range is the distribution of metric values across all of the available data. The goal is to eliminate metrics that have very small ranges (e.g., richness metrics based on only a few taxa) or that have similar values at most sites (e.g., most sites have values ¼ 0). A small range could indicate that a metric might not vary sufficiently across sites to discriminate among sites in different conditions. |
Natural gradient adjustment | Redundancy check |
Reproducibility (Signal/Noise) ?Comment:S/N= Signal to Noise The use of metrics that have relatively stable values at individual sites helps ensure that between-site differences in individual samples are caused by differences in stream condition rather than by sampling variation within a site. Sampling variation is estimated from repeat visits to individual sites. Available measures of sampling variation reflect several sources of variability (i.e., short-term indexperiod temporal variability, spatial variability within the reach, and laboratory variability). Low sampling variation is necessary if a metric is to have a highprobability of discriminating between sites in good and poor condition, and sampling variation should be small relative to the size of the among-site differences to be discriminated. We quantify metric reproducibility with a variant of the signal:noise ratio (S/N). S/N is the ratio of the variance among all sites (signal) to the variance of repeated visits to the same site (noise) (Kaufmann et al. 1999). Metrics with high S/N values are more likely to show consistent responses to stressors than are metrics with low S/N values. A metric that is perfectly correlated with a hypothetical stressor and that has no sampling variability will have an R2 ¼ 1.0 for that stressor. As S/N decreases, the maximum possible R2 value of the regression decreases because the sampling variability of the metric increases. When S/N ¼ 1, a perfect correlation between the metric and the stressor would produce R2 ¼ 0.5 (Fig. 2). We have no fixed threshold below which we eliminate metrics based on S/N. However, S/N values 1 indicate that visiting a single site twice yields as much metric variability as visiting 2 different sites. |
Responsiveness ?Comment:The ultimate test of the effectiveness of a metric is its ability to distinguish degraded from relatively undisturbed streams. A more general approach is to base the evaluation of responsiveness on the ability of a metric to distinguish least-disturbed (reference) from most-disturbed sites. |
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Variability Expression Given?
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Not applicable | Not applicable | Not applicable | Not applicable | Not applicable |
Variability Metric
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None | None | None | None | None |
Variability Value
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None | None | None | None | None |
Variability Units
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None | None | None | None | None |
Resampling Used?
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Not applicable | Not applicable | Not applicable | Not applicable | Not applicable |
Variability Expression Used in Modeling?
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Not applicable | Not applicable | Not applicable | Not applicable | Not applicable |
Variable ID
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Validated?
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Validation Approach (within, between, etc.)
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Validation Quality (Qual/Quant)
variable.detail.validationQualityHelp
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Validation Method (Stat/Deviance)
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Validation Metric
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Validation Value
variable.detail.validationValHelp
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Validation Units
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Use of Measured Response Data
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