Glossary
Below are some terms you'll find throughout this application.
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Accuracy | A property of a set of Measurements or estimates of being close to the exact or true value of what you're trying to measure. (Source: OECD). When playing darts, Accuracy is hitting the bullseye; whereas Precision is repeatedly hitting the same area of the board. | ||||||||||||||||||||||||||||||||||
Adaptive Management | "Adaptive management, ... formulates management policies as experiments that probe the responses of ecosystems as people's behavior in them changes. (This experimental emphasis is called "active" adaptive management in Walters and Holling (1990)."
Lee, K. N. 1999. Appraising adaptive management. Conservation Ecology 3(2): 3. [online] URL: http://www.consecol.org/vol3/iss2/art3/ "...adaptive management as a strategy for natural resource management can be traced to the seminal work of Holling (1978), Walters (1986), and Lee (1993). These scholars have framed and articulated the idea of an approach that treats on-the-ground actions and policies as hypotheses from which learning derives, which, in turn, provides the basis for changes in subsequent actions and policies." Stankey, George H.; Clark, Roger N.; Bormann, Bernard T. 2005. Adaptive management of natural resources: theory, concepts, and management institutions. Gen. Tech. Rep. PNW-GTR-654. Portland, OR: U.S. Department of Agriculture, Forest Service, Pacific Northwest Research Station. 73 p. https://www.fs.fed.us/pnw/pubs/pnw_gtr654.pdf |
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Archived | Archived is a status (State Diagram) attributed to Methods and Protocols that are incomplete, have not been in used/updated for over 18 months, and have not been versioned. Archived documents can return to a draft status only by the owner of the method or protocol of concern. Archived documents are hidden from all users other than the owner. | ||||||||||||||||||||||||||||||||||
Area of Inference | A geographical area or biological population on which you are deriving Indicators from Metrics according to the Inference Design. | ||||||||||||||||||||||||||||||||||
Attribute | A property that describes a data element or entity. In a database, this is often stored as a "field" in a table for a specific entity. For example sites within a master sample have a wide range of attributes (may be continuous or categorical), which can be used to winnow or select a subset of the sites. Attributes can also be used to stratify a sample design. While some people refer to data collected in the field or created as a result of analyzing or synthesizing field data as "attributes", in Monitoring Resources we use the terms measurements, metrics, and indicators to differentiate these types of data. |
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Auxiliary variable | If a variable that is known for every unit of the target population is not a variable of interest but is instead employed to improve the sampling plan or to enhance estimation of the variables of interest, it is called an auxiliary variable. (Source: Encyclopedia of Survey Research Methods) Auxiliary variables are "extra" variables measured in association with the desired response variable that might be used to increase precision of the estimate. For example, developing a modeled relationship between the response variable and auxiliary variables might be measured at more sites than can be monitored for the primary response variable. Auxiliary variables are used in model assisted surveys to guide the selection of the sample sites. |
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Bias | An effect which deprives a statistical result of representativeness by systematically distorting it, as distinct from a random error which may distort on any one occasion but balances out on the average. The bias of an estimator is the difference between its mathematical expectation and the true value it estimates. In the case it is zero, the estimator is said to be unbiased. (Source: OECD). | ||||||||||||||||||||||||||||||||||
Biased Sample | A sample obtained by a biased sampling process - a process which incorporates a systematic component of error, as distinct from random error which balances out on the average. Non-random samples are often, though not inevitably, subject to Bias, particularly when entrusted to subjective judgement on the part of human being. Source: OECD Opportunistic Samples are a type of Biased Sample. Contrast with Unbiased Samples -- both Probability Samples and Census. |
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Category | A classification rank used for summarizing and reporting that is below Subject, above Subcategory. For example, Fish or Water Quality. The Subject -> Category -> Subcategory taxonomy provides a series of pick lists for Protocol authors. After selecting a Subcategory, authors then enter a title for their specific Metric or Indicator. |
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Causal Mechanism | The process by which a cause or treatment (i.e., stressor or set of stressors) results in a change. | ||||||||||||||||||||||||||||||||||
Census | A survey conducted on the full set of observation objects belonging to a given Target Population or universe (aka {Statistical Population}. Source: OECD. A Monitoring Project conducting a "partial (or restricted)" census observes only members within its study area. For example, all members of a salmonid population within a subwatershed. Contrast with Probability Sample and Opportunistic Sample. |
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Confidence Interval | A confidence interval is an interval which has a known and controlled probability (generally 95% or 99%) to contain the true value. Source: OECD | ||||||||||||||||||||||||||||||||||
Continuous random variable | A random variable where the data can take infinitely many values. For example, a random variable measuring the time taken for something to be done is continuous since there are an infinite number of possible times that can be taken. Contrast with discrete random variable. | ||||||||||||||||||||||||||||||||||
Control | In an experiment, a control group is a baseline group that receives no treatment or a neutral treatment. To assess treatment effects, the experimenter compares results in the treatment group to results in the control group. |
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Customized Method | A modification of an existing Method (owned by a user other than you) to describe minor changes necessary to meet the needs of your project or program. The original Method details are preserved, along with annotations of the changes you will make when implementing the method. Customized Methods can only exist in the context of a specific Protocol. For example, you may see an existing method describing a technique for measuring substrate that matches most of what you do, except the existing method measures substrate at 10 intervals along each transect and your method only measures substrate at 5 intervals along each transect. Rather than create a new method, you can add the existing method to your protocol and then customize the method and make a note about the change from 10 to 5 intervals. |
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Data Repository | A storage space or container for monitoring or research data that may include Measurements, Metrics, and/or Indicators. Typically repositories are set up by Organizations to hold data generated by one or more Monitoring Programs; however, some repositories hold data from multiple organizations and/or monitoring programs and some don't hold raw data, but instead offer summaries of data, such as technical reports, publications, or figures/graphs displaying data. Ideally, these repositories are online relational databases (not just text files or spreadsheets) and accessible to the public, or at least accessible via a user account (that requires logging in). A single data set generated by a Method does not constitute an Data Repository. Note: In monitoringresources.org, we now call these "Environmental Information Repositories" the updated name more accurately reflects the types of data the monitoring community is interested in tracking. You can view the full list of Environmental Information Repositories. |
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Dataset | A collection of data, usually presented in tabular form. Each column represents a particular variable. Each row corresponds to a given member of the data set in question. It lists values for each of the variables, such as height and weight of an object. Each value is known as a datum. The data set may comprise data for one or more members, corresponding to the number of rows. Nontabular data sets can take the form of marked up strings of characters, such as an XML file. Source: Wikipedia |
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Deconvolution | Procedure to remove impact (bias) of metric uncertainty on an indicator estimated cumulative distribution or percentiles estimated for target population and sub-populations. | ||||||||||||||||||||||||||||||||||
Discovery Level Metadata | Metadata records that typically provide a minimum of essential information to enable a user to find out if a particular dataset exists, its location and ownership, and how to obtain further information. Contrast with full metadata include additional information on such aspects as data quality and lineage (provenance) and technical details for access and exploitation. Source: GBIF |
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Discrete random variable | A variable that may assume any of a specified list of exact values that are numerical outcomes of a random phenomenom (Source Yale Stats) Contrast with continuous random variable. | ||||||||||||||||||||||||||||||||||
Effectiveness Monitoring | Effectiveness monitoring is used to determine whether the action achieved the ultimate objective. For example, was the ecosystem restored to reference conditions? Effectiveness monitoring requires response variables to be clearly articulated so that they can be measured accurately and precisely. Typical response variables for wildlife are related to species’ habitats or populations (Block et al. 2001:294).
Block et al. 2001. Design and Implementation of Monitoring Studies to Evaluate the Success of Ecological Restoration on Wildlife. Restoration Ecology Vol. 9 No. 3, pp. 293–303. Morrison, ML and BG Marcot. 1995. An Evaluation of Resource Inventory and Monitoring Program Used in National Forest Planning. Environmental Management Vol. 19, No. 1, pp. 147-156. |
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Element of a Population | Elements of a population refer to the ‘parts’ that make up the target population. Elements of a discrete population are easy to describe in that they are the individuals that make up the population. Each lake or wetland in a population of lakes or population of wetlands is a population element. For continuous resources, population elements are points on the target resource, e.g., points on a stream network. An important rule in the definition of the population elements is its explicit definition so that members of a field crew can determine whether the site visited is a member of the target population. | ||||||||||||||||||||||||||||||||||
Endorser Organization | An Organization that reviews and sanctions a Protocol. | ||||||||||||||||||||||||||||||||||
Environmental Information Repository | A storage space or container for monitoring or research data that may include Measurements, Metrics, and/or Indicators. Typically repositories are set up by Organizations to hold data generated by one or more Monitoring Programs; however, some repositories hold data from multiple organizations and/or monitoring programs and some don't hold raw data, but instead offer summaries of data, such as technical reports, publications, or figures/graphs displaying data. Ideally, these repositories are online relational databases (not just text files or spreadsheets) and accessible to the public, or at least accessible via a user account (that requires logging in). A single data set generated by a Method does not constitute an Environmental Information Repository. Note: In monitoringresources.org, we used to call these "Data Repositories" but updated the name to more accurately reflect the types of data the monitoring community is interested in tracking. You can view the full list of Environmental Information Repositories. |
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Experimental Design | The process of planning a study that uses manipulation and controlled testing to understand causal processes. Planning an experiment properly is very important in order to ensure that the right type of data and a sufficient sample size and power are available to answer the research questions of interest as clearly and efficiently as possible. From: www.experiment-resources.com/experimental-research.html |
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Frame Evaluation | In advance of the field season, sample sites are reviewed individually to ensure that they are a member of the design’s target population. For example, a point that lies upstream of an impassable fish barrier would be rejected in a design where the target population included all anadromous stream reaches. May involve a visit to the site in advance of data collection activities to determine whether the site is target or not. | ||||||||||||||||||||||||||||||||||
Full Metadata | Metadata records that include additional information on such aspects as data quality and lineage (provenance) and technical details for access and exploitation. Contrast with discovery level metadata which typically provides a minimum of essential information to enable a user to find out if a particular dataset exists, its location and ownership, and how to obtain further information. Source: GBIF |
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Funder Organization | An Organization that pays for the development of a Protocol or that simply funds Monitoring Programs or individual projects that use Protocols. In monitoringresources.org, a Funder Organization can "approve" one or more Protocols for use within its program. | ||||||||||||||||||||||||||||||||||
Generalized Random-Tessellation Stratifed (GRTS) Design | The generalized random-tessellation stratified design commonly referred to as a GRTS design is an algorithm that creates a spatially well-balanced, random selection of sites across 1-dimensional systems (e.g., linear resources such as stream networks), 2-dimensional systems (e.g., areal resources such as forests), or 3-dimensional systems (3-D resources such as oceans or lakes). Source Stevens & Olsen 2004 | ||||||||||||||||||||||||||||||||||
Geostatistics | A branch of statistics focusing on spatial or spatiotemporal datasets (Source Wikipedia). The term was introduced by Matheron (1962) for the study of ‘regionalized variables’; that is, variables supposed to follow some spatial stochastic process (ISI). | ||||||||||||||||||||||||||||||||||
Horvitz-Thompson (HT) Estimator | A method of estimating the population total when sampling without replacement from a finite population and when unequal probabilities of selection are used. The estimator is unbiased, linear and can be used with a variety of basic sample designs (ISI; Horvitz and Thompson, 1952). | ||||||||||||||||||||||||||||||||||
Hydrologic Unit Code (HUC) | The United States is divided and sub-divided into successively smaller hydrologic units which are classified into four levels: regions, sub-regions, accounting units, and cataloging units. The hydrologic units are arranged within each other, from the smallest (cataloging units) to the largest (regions). Each hydrologic unit is identified by a unique hydrologic unit code (HUC) consisting of two to eight digits based on the four levels of classification in the hydrologic unit system. (Source USGS) | ||||||||||||||||||||||||||||||||||
Implementation Monitoring | One type of monitoring, or purpose, this assesses whether a directed management action was carried out (implemented) as designed. This type determines whether established guidelines are being followed and whether management operations are being conducted as prescribed (Morrison and Marcot 1995). In the context of restoration, implementation monitoring quantifies changes immediately after treatments, and evaluates whether treatments were done, i.e. implemented, as prescribed (Block et al. 2001). This type of monitoring checks whether a minimum level of performance is being met as determined by the standard, and is communicated in the form of compliance monitoring indicators. Indicators derived from compliance monitoring can be used to prevent, minimize or mitigate negative environmental and social impacts of resource management (Hooper et al. 2015, Savilaakso et al. 2015). Block et al. 2001. Design and Implementation of Monitoring Studies to Evaluate the Success of Ecological Restoration on Wildlife. Restoration Ecology Vol. 9 No. 3, pp. 293–303. Morrison, ML and BG Marcot. 1995. An Evaluation of Resource Inventory and Monitoring Program Used in National Forest Planning. Environmental Management Vol. 19, No. 1, pp. 147-156. |
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Inclusion Probability | The probability of an element or member of the statistical population (e.g. a site) becoming part of the sample during the drawing of a single sample. Inclusion Probability is the inverse of the statistical weight. (Source: OECD). |
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Indicator | Value resulting from the data reduction of Metrics across sites and temporal periods based on applying the procedures in the Inference Design. A reported value used to indicate the status, condition, or trend of a resource or ecological process; intended to answer questions posed by the Objectives of the Protocol. Contrast with Metric. For example, measurement of channel migration (metric) + over a period of time (metric) = Channel Migration Rate (indicator) Per the Inference Design, Metrics are combined or reduced to produce Indicators. |
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Inference Design | Component of the Study Plan that defines the process of determining Indicator values based on Metric values observed at sites during specific temporal units over the course of the study. Contrast with Response Design. NOTE: monitoringresources.org will not support detailed documentation of Inference Design; however users may add Data Analysis/Interpretation Methods to their Protocol that explain how Metrics are combined to produce Indicators. |
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Key Assumption | Something that is accepted as true or as certain to happen, without proof. It is important to document Key Assumptions when you write your Study Plan. Example:
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Landowner Permission Evaluation | For sample sites on private lands or sample sites that require traversing private lands, the landowner must be contacted to obtain permission to access the site. A landowner permission evaluation documents the results of the landowner contact. | ||||||||||||||||||||||||||||||||||
Local Neighborhood Variance (LNV) Estimator | The LNV is an alternate to the Horvitz-Thompson (HT) Estimator or other variance estimators applied to sample surveys. The LNV provides an unbiased estimate of variance if spatial designs (such as GRTS) are used, especially if the response of interest exhibits spatial pattern. | ||||||||||||||||||||||||||||||||||
Margin of Error | "Radius" (or half the width) of a confidence interval for a particular statistic from a survey. Source: Wikipedia | ||||||||||||||||||||||||||||||||||
Master Sample | The full list of sites that would be sampled with a complete Census used to generate a Random Sample of sites for a Probability Sample. These sites can be used for comparable, complementary monitoring among separate monitoring organizations and across geographic scales. A Master Sample retains the principles of Randomization and Spatial Balance. For further reading: Larsen, D.P., A.R. Olsen, and D.L. Stevens. 2008. Using a master sample to integrate stream monitoring programs. JABES 13: 243-254. |
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Measurement | A value resulting from a data collection event at a specific Site and temporal unit. Measurements can be used to produce Metrics using a Response Design. Per the Response Design, Measurements are combined or reduced to produce Metrics. |
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Metadata | Metadata describe information about a dataset, including who, what, where, when, why, and how, so that it can be understood, re-used, and integrated with other datasets. Metadata records follow a standard format to enable interoperability. Why metadata? Metadata are crucial for any use or reuse of data; no one can responsibly re-use or interpret data without metadata that explains how the dataset was created, why, where it is geographically located, and details about the structure of the data. Uses for Metadata: Metadata are used for enabling data discovery, understanding data, analysis and synthesis, maintaining longevity of a dataset, tracking the progress of a research project, and demonstrating the return on investment for research at an institution. Source: USGS Data Management|Metadata page Recommended Reading
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Metadata Record | A metadata record is a file of information, usually presented as an XML document, which captures the basic characteristics of a specific dataset, data entity, monitoring project, or other item. For more on this topic, see our definition for metadata. In Monitoring Resources' Metadata Builder, we attempt to only generate ISO 19115: 2003 compliant discovery level metadata records for one dataset at a time rather than full metadata records. |
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Method | A systematic, standard operating procedure for collecting data (Measurements) or analyzing data. Each method must be: 1. documented as one procedure in a step-wise manner, 2. repeatable by others. In MonitoringResources.org Methods are of two Method Types: Data Collection or Data Analysis. Methods have a "State" or status - of Draft, Finalized, or In Review (see our State Diagram). Methods describe how to derive Metrics from Measurements, or Indicators from synthesizing or summarizing metrics over space or time. Methods are listed in a protocol to explicitly describe how the protocol objectives will be met. |
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Method Type | A classification of a Method based on its function, such as Data Collection or Data Analysis. | ||||||||||||||||||||||||||||||||||
Method Unit | The standard unit of measure used by the method. Options include Metric, English, or Mixed. We urge Method Owners to not use the "Mixed" option if at all possible. | ||||||||||||||||||||||||||||||||||
Metric | A value resulting from the reduction or processing of Measurements taken at a Site and temporal unit at one or more times during the study period based on the procedures defined by the Response Design. Metrics can be used to estimate an Indicator using an Inference Design. Note that a variety of Metrics can be derived from original Measurements. Per the Response Design, Measurements are used to produce Metrics. Per the Inference Design, Metrics are used to produce Indicators. |
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Model | A formalized expression of a theory or the causal situation which is regarded as having generated observed data. Source: OECD | ||||||||||||||||||||||||||||||||||
Model Based Design | A model-based spatial design relies on selection of sites based on the need to estimate parameters or coefficients of a model that will be used to make the population estimates. Such models typically include one or more independent variables or covariates such as environmental conditions or habitat quality. Sites are generally selected along the important gradients governing the model parameters. A simple model might be a relationship between a population’s growth rate and temperature. Sites might be selected at locations covering a thermal gradient over the range of the population’s thermal tolerance. Then the model would be used to estimate productivity across all sites in the domain. A restricted model-based spatial design refers to situations in which the selection of locations in part of the domain is guided by the candidate model, and locations in other parts are selected by other methods | ||||||||||||||||||||||||||||||||||
Monitoring Metadata Exchange (MMX) | The Monitoring Metadata Exchange (MMX) is a data exchange standard used to define and exchange metadata and location information associated with data collection events. The MMX enables better integration of information from disparate efforts across time and space by providing data seekers with more than just a location of monitoring efforts; it helps answer the 'who', 'what', 'where', 'when', and 'how' about specific projects. Any project can use the MMX standard to exchange data with MonitoringResources.org and any website with map services can use the exchange to increase their content. If your project is interested in using the MMX standard to automate the exchange of information, please contact pnamp.info@gmail.com, or find the full documentation on the MMX standard here. | ||||||||||||||||||||||||||||||||||
Monitoring Program | Activities led and sponsored by an Organization to collect and/or analyze natural resources or environmental data with stated objectives to implement one or more Monitoring Projects. Monitoring Programs use a set of Protocols to collect and/or analyze monitoring data for sites in multiple geographic locations in response to a research question, or to meet an agency mission or mandate. Examples: EMAP, Washington Forum on Monitoring, AREMP, BPA's RM&E Program. Monitoring Programs can have one or more Protocols, and Protocols can be shared by many Monitoring Programs |
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Monitoring Project | Activities led and sponsored by an Organization to collect and/or analyze natural resources or environmental data for one or more Monitoring Purposes. Monitoring Programs can have one or more Monitoring Projects which typically have budgets, durations, and specific outputs. | ||||||||||||||||||||||||||||||||||
Monitoring Type | The primary purpose of your research or Monitoring Program. These monitoring purposes, or types can overlap (Block et al. 2001). Some of the most recognized types are: WM Block, Franklin, AB, Ward, JP Jr., et al. 2001. Design and Implementation of Monitoring Studies to Evaluate the Success of Ecological Restoration on Wildlife. Restoration Ecology. Vol. 9 No. 3, pp. 293–303. |
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Multi-Density Category | Defines a subset of the sample frame that will have the same probability of selection for all elements in that subset. Multi-density categories partition the sample frame into mutually exclusive and exhaustive subsets where the probability of selection will be constant for all elements within a subset. Density refers to the density of sample points (i.e., sites) within a category. Compare to Stratum. | ||||||||||||||||||||||||||||||||||
Non-random Sample | A sample selected by a non-random method. For example, a scheme whereby units are selected purposively would yield a non-random sample. Again, a sample obtained by taking members at fixed intervals on a list is a non-random sample unless the list was arranged in a random order. Source: OECD | ||||||||||||||||||||||||||||||||||
Objective | A formal statement detailing a desired outcome of a Project. A good objective meets S.M.A.R.T. criteria: Specific, Measurable, Achievable, Results-oriented, Time-limited (Doran, GT 1981). If the project is well conceptualized and designed, realization of a project’s objectives should lead to the fulfillment of the project’s goals (described in the Study Plan). In MonitoringResources.org, an important aspect of documenting a Protocol is defining one or more objectives, then describing metrics and indicators to meet every objective, then documenting the data collection and analysis methods that will be used to achieve each metric or indicator. |
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Opportunistic Design | A type of Biased Sample. Common reasons given for opportunistic sampling are Ease of Access and/or Historic Precedent. Contrast with Probabilistic Design and Census. | ||||||||||||||||||||||||||||||||||
Organization | A formal entity such as a tribe or tribal consortium; non-profit, business or consulting firm; or federal, state or regional agency; that has staff and a budget. Examples: Oregon Department of Fish and Wildlife (ODFW), Nez Perce Tribe, Environmental Protection Agency (EPA), Tetra Tech, Bonneville Power Association (BPA). In MonitoringResources.org, some organizations have special functions: Sponsor Organization, Funder Organization, Endorser Organization. | ||||||||||||||||||||||||||||||||||
Oversample | coming soon | ||||||||||||||||||||||||||||||||||
Owner | The person responsible for maintaining a primary entity, such as a Protocol or Method, in monitoringresources.org. Normally, this is the same as the Creator and Author, but doesn't have to be. | ||||||||||||||||||||||||||||||||||
Panel | A set of Sites that have the same revisit pattern across years. For example, a set of sites visited every year would make up one panel. A set of sites visited every three years would make up a second panel. | ||||||||||||||||||||||||||||||||||
Power | In general, the power of a statistical test of some hypothesis is the probability that it rejects the null hypothesis when that hypothesis is false (ISI). | ||||||||||||||||||||||||||||||||||
Power Analysis | Power analysis is a statistical approach to determining the required sample size to obtain population estimates within a given confidence interval. Power analysis generally requires estimates of the distribution of the population to be sampled and in some cases a determination of analytical tools to be applied. To learn more, visit http://www.statsoft.com/textbook/power-analysis or http://en.wikipedia.org/wiki/Statistical_power. |
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Precision | A property of a set of Measurements of being very reproducible or of an estimate of having small random error of estimation. (Source: OECD). Precision is a quality associated with a class of Measurements and refers to the way in which repeated observations conform to themselves; and in a somewhat narrower sense refers to the dispersion of the observations, or some measure of it, whether or not the mean value around which the dispersion is measured approximates the "true" value. Contrast with Accuracy. | ||||||||||||||||||||||||||||||||||
Probabilistic Design | A sampling design in which you select sample locations by a method based on the theory of probability (random process), that is, by a method involving knowledge of the likelihood of any unit being selected. Source: OECD Examples of probabilistic design include Simple Random Sample and GRTS. Contrast with Biased Sample and Census. |
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Protocol | "A detailed plan that explains how data are to be collected, managed, analyzed, and reported, and is a key component of quality assurance for natural resource monitoring programs" (Oakley et al. 2003). Protocols are necessary to ensure that changes detected by monitoring actually are occurring in nature and not simply a result of measurements taken by different people or in slightly different ways. Required sections of protocols are: Background/Rationale to explain why you use these particular methods to meet your specific Objectives, and Methods and Metrics to describe how you meet the objectives. Also required is Metric-Method Mapping. Sections not required, but important for future repeatability, and metadata accessibility, are: Figures and forms, and Additional details you can upload, Literature Cited, and a self-citation. Protocols can belong to many Monitoring Programs. Protocols have "States" or a status of Draft, In Review, or Finalized (State Diagram). In November 2017, Study Plans were extracted from Protocols. If you owned a draft protocol at that time, your Study Plan information was saved, extracted and can be found in the list of Study Plans or under your account name. |
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Purposive Sample | A sample in which the individual units are selected by some purposive method. It is therefore subject to biases of personal selection and for this reason is now rarely advocated in its crude form. Source: OECD | ||||||||||||||||||||||||||||||||||
Random Sample | A sample which has been selected by a method of random selection. Source: OECD Random sampling allows each element of the target population (as represented by the Sample Frame) a positive chance of being selected in the sample. This likelihood of being selected is the inclusion probability (or inclusion density for continuous populations); its inverse is the sample weight. | ||||||||||||||||||||||||||||||||||
Randomization | An important technique in probability samples or designs that has two functions: guards against selection bias, intentional or otherwise, and it provides an objective, inferential basis for extrapolating from the sample to the target population level. (Source: Sample Design, Execution, and Analysis for Wetland Assessment, Stevens and Jensen, 2007.) | ||||||||||||||||||||||||||||||||||
Reference Site | A reference site (aka 'control site') is a spatial/temporal location that is similar (ideally identical) to another site, the only difference being that the other site is affected to a greater (or lesser) extent by some mechanism. Of course, no two sites can be identical, but the careful choice of one or more reference sites will permit reasonably rigorous conclusions about differences in responses at those sites to the Causal Mechanism. More information on reference and control sites and the different uses of these terms can be found in Downes et al. (2002, page 122) and Roni et al. (2005, page 22). | ||||||||||||||||||||||||||||||||||
Remote Sensing | The acquisition of information about an object or phenomenon, without making physical contact with the object. In modern usage, the term generally refers to the use of aerial sensor technologies to detect and classify objects on Earth (both on the surface, and in the atmosphere and oceans) by means of propagated signals (e.g. electromagnetic radiation emitted from aircraft or satellites). From: wikipedia |
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Replicate | In engineering, science, and statistics, replication is the repetition of an experimental condition so that the variability associated with the phenomenon can be estimated. ASTM, in standard E1847, defines replication as "the repetition of the set of all the treatment combinations to be compared in an experiment. Each of the repetitions is called a replicate." Replication is not the same as repeated measurements of the same item: they are dealt with differently in statistical experimental design and data analysis." | ||||||||||||||||||||||||||||||||||
Resilience | The capacity of a natural system to recover from disturbance. Source: OECD For instance, imagine two lakes, one that includes only a small number of species and/or functional groups of phytoplankton, zooplankton, and fish, and another thathas multiple species and/or functional groups in each of those categories. The simple lake ecosystem will probably be less able to maintain its previous structure and function after major disturbances such as massive nutrient loading, warming, or changes in seasonal timing of events than the second lake. An often-forgotten second component to the resilience concept that Holling (1972) described is that frequent disturbances help select for characteristics among component populations that lead to greater resilience. |
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Response Design | The Response Design is a component of a Study Plan: what and how Measurements will be made (field or laboratory methods) and data analysis/interpretation Methods used to derive Metrics from Measurements as determined by the Spatial Design and Temporal Design. In MonitoringResources.org, describe the response design in the background of the Study Plan. Describe detailed methods in the Protocol, and describe the spatial and temporal designs in the Sample Design
Response Design includes Methods, Measurements, and Metrics. In MonitoringResources.org, Methods and Metrics are components of the Protocol. Want to learn more? check out monitoringadvisor.org "There are two conceptually separate and distinct design activities involved here. One design effort is determining what to measure, count, or observe given that we are at some point in the population domain, and how to combine or synthesize the measurements, counts, or observations collected. This effort is response design: the process of deciding what to measure and how to measure it; of designing and giving substance to the quantity or quantities we associate with the point. The other design activity is sampling design: the process of specifying how and where to select population units or points on the response surface. The response at these points will be used to estimate attributes of the response surface, which, if we have done the response design correctly, will bear some known relationship to the attributes of the population of real interest.These two processes are conceptually distinct, but often are confused in practice.The task of finding suitable and efficient ways to sample a spatial environmental population by exploiting its spatial component is greatly simplified if we keep these two processes operationally distinct. The benefit of doing so is that we can develop efficient and practical response designs that exploit the local characteristics of the population, and develop efficient sampling designs that exploit the regional characteristics of the population. We then appeal to sampling theory to establish design-unbiasedness of proposed estimators of the response surface parameters, and appeal to the response design to establish the link between the response surface parameters and population parameters." --- Stevens and Urquhart, 2000. Environmetrics |
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Safety Evaluation | In advance of the field season, sample sites are evaluated by crew members to ascertain whether the site can be safely accessed by the crew. Reasons for rejecting a site for safety reasons could include hazardous terrain, excessive distance from an access road or trail, or other conditions where crew safety cannot reasonable be assured. | ||||||||||||||||||||||||||||||||||
Sample Design | "Sample design" is sometimes used in a clearly defined sense, with reference to a given frame, as the set of rules or specifications for the drawing of a sample in an unequivocal manner (The International Statistical Institute, "The Oxford Dictionary of Statistical Terms", edited by Yadolah Dodge, Oxford University Press, 2003). As a component of MonitoringResources.org, the Sample Design area contains a link to a Study Plan. It is the documentation of the spatial and temporal designs applied to data collection and analysis; including a spatial design that describes where metrics will be determined and how and why locations were chosen, and a temporal design that is the total duration of the entire study, and the frequency of sampling sites. The Sample Design component allows uploading of sampling sites, and sharing of sampling sites (user sample files) that exist in the system. It has sections to characterize sampling locations, sampling event details, and specific spatial and temporal assignments of locations to rotating panels for alternating visits, treatment categories or strata, and blocks (strata by panels). Several Sampling Designs are available to describe how you sample sites, including a Generalized Random Tessellation Stratified (GRTS) design. The GRTS design section uses an algorithm to generate sampling sites to randomly assign sites from a larger pool of sites. |
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Sample Frame | Representation of the target resource used in the selection of the sample. For discrete populations, the frame is the list containing each population element, the list of lakes or streams in the region of interest, sometimes referred to as a "list frame" (e.g. list of all lakes in Alaska). For continuous resources, such as stream networks, a digital map of the stream network is the usual form of the frame. Accurate representations of stream networks therefore become critical as they become the functional target population. | ||||||||||||||||||||||||||||||||||
Sample Survey | A sample survey is a survey which is carried out using a sampling method, i.e. in which a portion only, and not the whole target population is surveyed (Source: OECD). Sample surveys rely on selecting part of the resource of interest, characterizing that part, and then making inferences to the entirety. Sample surveys are especially useful if a census of the resource cannot be conducted (i.e., too expensive; too time consuming; technically not feasible). |
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Sampling Error | That part of the difference between a population value and an estimate thereof, derived from a random sample, which is due to the fact that only a sample of values is observed; as distinct from errors due to imperfect selection, bias in response or estimation, errors of observation and recording, etc. The totality of sampling errors in all possible samples of the same size generates the sampling distribution of the statistic which is being used to estimate the parent value. Sampling errors arise from the fact that not all units of the targeted population are enumerated, but only a sample of them. Therefore, the information collected on the units in the sample may not perfectly reflect the information which could have been collected on the whole population. The difference is the sampling error (Eurostat, Quality Glossary). Source: OECD |
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Sampling Unit | The specific area or point where Measurements are taken. For natural resources like lakes, wetlands, or streams, the Sampling Unit may be a lake, a portion of the wetland, or a point on a stream. Statisticians define these as the elements that represent the target population. The Spatial Design selects the study's Sites and Sampling Units. | ||||||||||||||||||||||||||||||||||
Simple Random Sample | Sampling in which every member of the Target Population has an equal chance of being chosen (Inclusion Probability) and successive drawings are independent as, for example, in sampling with replacement. Source: Source: OECD One downside to simple random samples is that they tend to "clump" sample sites, producing a sample that is not spatially-balanced. To overcome this limitation, consider using a GRTS design. |
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Site | The spatial location where one or more Measurements are taken and Metrics derived. A more generic term for this is spatial unit. The Spatial Design component of the Study Plan determines the number and arrangement of Sites; the Temporal Design component determines the revisit patterns and Panel assignments for Sites. One example of a Site is a dam where fish are counted. Another example is a specific reach or length of stream where spawning salmon are counted or habitat is surveyed and summarized. | ||||||||||||||||||||||||||||||||||
Spatial Balance | The idea that sample points be distributed in some regular or nearly regular pattern, so they are more or less evenly dispersed over the extent of the resource of interest. (Source Stevens & Olsen 2004) | ||||||||||||||||||||||||||||||||||
Spatial Design | Component of Study Plan that defines where in the study region metrics will be determined (how you select which sites to monitor in the study area).
Spatial designs describe how sampling effort is to be allocated across a study area. The most appropriate spatial design for you depends on your monitoring requirements, monitoring design characteristics, and monitoring constraints.
Listed are a few of the spatial designs available:
Categories of Spatial Design
Want to learn more? check out monitoringadvisor.org |
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Spatial Domain | The geographic region over which a survey or study is to be conducted. | ||||||||||||||||||||||||||||||||||
Spatial Unit | A more technical, statistical term for Site. Compare with Temporal Unit. | ||||||||||||||||||||||||||||||||||
Sponsor Organization | The Organization that generates or develops a Protocol. | ||||||||||||||||||||||||||||||||||
Spring Transition | The time of year when productivity of phytoplankton and zooplankton at the bottom of the salmon food chain in the ocean greatly increases due to mixing of nutrient-rich waters at depth with surface waters that are exposed to sunlight. | ||||||||||||||||||||||||||||||||||
State Diagram | In MonitoringResources.org Protocols and Methods have a State or status. The diagram illustrates possible states: |
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Statistical Population | The total membership or population or “universe” of a defined class of people, objects or events. Source: OECD | ||||||||||||||||||||||||||||||||||
Status and Trend Monitoring | Status monitoring of an ecologically degraded site first characterizes existing or pre-restoration biotic and abiotic conditions-the baseline status, essential to help define restoration actions and to allow comparisons post-restoration implementation. (Hooper et al. 2015). This monitoring is appropriate If no specific action is being considered and the purpose is to characterize changes of the state of a system over time-the trend (Reynolds et al. 2016). For example, what is the density of sage grouse within a sagebrush ecosystem over a given period of time? | ||||||||||||||||||||||||||||||||||
Strahler Order | In the application of the Strahler stream order to hydrology, each segment of a stream or river within a river network is treated as a node in a tree, with the next segment downstream as its parent. When two first-order streams come together, they form a second-order stream. When two second-order streams come together, they form a third-order stream. Streams of lower order joining a higher order stream do not change the order of the higher stream. Thus, if a first-order stream joins a second-order stream, it remains a second-order stream. It is not until a second-order stream combines with another second-order stream that it becomes a third-order stream. To qualify as a stream a hydrological feature must be either recurring or perennial. Recurring streams have water in the channel for at least part of the year. The index of a stream or river may range from 1 (a stream with no tributaries) to 12. (Source Wikipedia) | ||||||||||||||||||||||||||||||||||
Stratification | Target populations can be divided into discrete subpopulations, or strata, on which to increase/decrease sample size. A stream network’s elevation could be used to divide the population into elevation strata, allocating an equal number of sites per stratum (likely yielding inclusion probabilities that vary by stratum because the amount of stream length in each stratum likely would vary). Stratification is the process of grouping members of the population into subgroups before sampling. The strata should be mutually exclusive and also collectively exhaustive so that no population element is excluded. (Source: OECD). | ||||||||||||||||||||||||||||||||||
Stratum | A subset of a statistical population for which an independent sample is selected. The term stratum is sometimes used to denote any division of the population for which a separate estimate is desired, i.e. in the sense of a domain of study. It is also used sometimes to denote any division of the population for which neither separate estimates nor actual separate sample selection is made. (Source: OECD). |
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Study Plan | A Study Plan is the umbrella component in MonitoringResources.org for documenting metadata for your program's monitoring effort or study. Required sections are a Monitoring Program, a link to a Protocol, a Background/Rationale (abstract) to describe overarching goals for the project, and Objectives to answer management or research questions for your entire study or monitoring effort. It also includes a Monitoring Purpose, Key Assumptions, Quality Control and Reporting, Personnel and Training, and Schedule and Budget sections. The study plan links to the separately documented components: a Protocol and a Sample Design.
In the Protocol component of MonitoringResources.org, you document Methods to define how Measurements are taken and Metrics are calculated so that you can estimate Indicators for target population and sub-populations. Where and when are documented in the Sample Design component of MonitoringResources.org. Within the Sample Design, define where you will sample locations in the Spatial Design, and when in the Temporal Design. In late 2017, Study Plans were extracted from Protocols. If you owned a draft protocol at that time, your Study Plan information was saved with the same name as the protocol from which it was extracted and can be found in the list of Study Plans or under your account name. | ||||||||||||||||||||||||||||||||||
Subcategory | A classification rank used for summarizing and reporting that is below Category. For example, Fish Abundance or Turbidity. The Subject -> Category -> Subcategory taxonomy provides a series of pick lists for Protocol authors. After selecting a Subcategory, authors then enter a title for their specific Metric or Indicator. |
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Subcategory Focus | Attributes of some Metrics and Indicators that help describe the data being collected or analyzed. For example "Fish Life Stage Strategy" is a Subcategory Fucus of the Indicator "Abundance of Fish" which allows people to differentiate juvenile from adult abundance data. Subcategory Foci then have two or more Subcategory Focus Options. For example, "Adult - Spawner" is one of the options under the Subcategory Focus "Fish Life Stage Strategy". | ||||||||||||||||||||||||||||||||||
Subcategory Focus Option | One of the possible values or selections for a given Subcategory Focus. For example, "Fish Life Stage Strategy" is a Subcategory Focus of the Indicator "Abundance of Fish" and it has various Subcategory Focus Options such as "Adult - Spawner" and "Adult-Outmigrant". | ||||||||||||||||||||||||||||||||||
Subject | A classification rank used for summarizing and reporting that identifies the broad area of study. For example, Biological or Chemical. The Subject -> Category -> Subcategory taxonomy provides a series of pick lists for Protocol authors. After selecting a Subcategory, authors then enter a title for their specific Metric or Indicator. |
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Subpopulation | A subset of the target population that is of interest for determining indicator value based on inference design. | ||||||||||||||||||||||||||||||||||
Systematic Design | An experimental design laid out without any randomization. The term is difficult to define exactly because in one sense every design is systematic; it usually refers to a situation where experimental observations are taken at regular intervals in time or space. Source: OECD Related: Systematic Sample |
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Systematic Sample | A sample which is obtained by some systematic method, as opposed to random choice; for example, sampling from a list by taking individuals at equally spaced intervals, called the sampling intervals, or sampling from an area by determining a pattern of points on a map. Source: OECD Contrast with Probability Sample designs: Simple Random Sample and GRTS Related: Systematic Design |
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Target Population | In statistical usage the term population is applied to any finite or infinite collection of individuals. It has displaced the older term ‘universe’…(ISI). The target population refers to the resource to be described. For example, the number of estimated fish of a given species of a specific population in a stream network in a particular watershed, the biological condition of streams and rivers in a state, or the habitat condition of streams in a national forest. Critical in developing the design is an explicit definition of the target population. The target population description contains specific information about the stream network: its spatial extent; flow status (the perennial network? Includes the intermittent channels?); its size (all stream sizes? Just first order streams?). Include enough specific information so that an individual could determine whether a location on a stream network includes part of the target population; in some cases, membership in the target population might be determined after data have been collected at the site. See "Establishing the Target Population" for guidance from EPA. |
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Temporal Design | Component of Study Plan that describes the total duration of the study (Temporal Domain) and the frequency that sites will be sampled during the study (Temporal Unit).
The Temporal Design describes the site revisit pattern for each temporal unit. A Panel is a set of sites that have the same temporal unit. A study may have only one panel,
but can also have many if the sites need to be revisited at different times during the course of the study. Categories of Temporal Design Complete Revisit - Every site is revisited on each sampling occasion. Never Revisit - A different site is visited on a given sampling occasion and never visited again. Opportunistic - Sites are selected and visited on a convenience basis. Complex - Sites are visited/revisited according to their assigned Panels; covers "Repeating", "Rotating", and "Split" panel designs. Want to learn more? check out monitoringadvisor.org |
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Temporal Domain | The temporal extent or duration of a study (aka study period). In monitoringresources.org, we ask Protocol owners to specify the planned or desired temporal domain of their study, rather than trying to keep track of the actual temporal domain which may change over time given the ups and downs of funding cycles. Temporal Domain and Temporal Unit are aspects of a study's Temporal Design. | ||||||||||||||||||||||||||||||||||
Temporal Unit | The interval during which Measurements are made at the Site, and subsequently the interval for which metric values could be determined. Inmonitoringresources.org, we ask Protocol owners to specify the minimum temporal unit of their study when documenting a complex Temporal Design which has multiple Panels. Both Temporal Domain and Temporal Unit are aspects of a study's Temporal Design. | ||||||||||||||||||||||||||||||||||
Trend | Long-term temporal pattern (i.e. change over time) in what you are monitoring. | ||||||||||||||||||||||||||||||||||
Unbiased Sample | A sample drawn and recorded by a method which is free from Bias. This implies not only freedom from bias in the method of selection, e.g. random sampling, but freedom from any bias of procedure, e.g. wrong definition, non-response, design of questions, interviewer bias, etc. An unbiased sample in these respects should be distinguished from unbiased estimating processes which may be employed upon the data. Source: OECD Contrast with Biased Sample. |
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User Site | Sites that are not drawn from one of the supported master samples, but have a history of data collection events that investigators wish to integrate into new sample designs. User sites may be part of an opportunistic sample or a probability sample (e.g. selected via a GRTS process). Integrating user sites into spatially distributed probabilistic designs based on GRTS may have important implications on the validity of your statistical design. You should seek professional advice prior to using user sites in your sample design. |
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Validation Research | One category of Monitoring Type. Controlled research can discover the mechanistic basis of baseline habitat variability and can then guide future remedial actions by enhancing the evaluation of causal relationships between a restoration action and a response. For example, validation investigations demonstrated reductions in sediment and associated nutrient loading in waterways adjacent to retired agricultural land with wetland restoration in the upper Mississippi basin. Variables used to validate the hypotheses were isotopic and elemental tracers in suspended sediments. Their presence demonstrated that cropland and stream bank soils accounted for a greater proportion of sediments in streams lacking adjacent conservation actions (Hooper et al. 2015:287; Williamson et al. 2014). Bonneville Power Association initially titled this category as "Uncertainties Research"; some projects were labeled as Uncertainties Research prior to 2017. | ||||||||||||||||||||||||||||||||||
Variance | The mean square deviation of the variable around the average value. It reflects the dispersion of the empirical values around its mean. Source: OECD | ||||||||||||||||||||||||||||||||||
Variance Analysis | (aka Variance Decomposition) The total variation displayed by a set of observations, as measured by the sums of squares of deviations from the mean, may in certain circumstances be separated into components associated with defined sources of variation used as criteria of classification for the observations. Such an analysis is called an analysis of variance, although in the strict sense it is an analysis of sums of squares. Many standard situations can be reduced to the variance analysis form. Source: OECD | ||||||||||||||||||||||||||||||||||
Water Resource Inventory Areas (WRIA) | Administrative and planning boundaries in the state of Washington. Washington Department of Ecology and other state natural resources agencies have divided the state into 62 Water Resource Inventory Areas or WRIAs to delineate the state's major watersheds. Ecology is responsible for the development and management of these areas. ((Source Dept. of Ecology) | ||||||||||||||||||||||||||||||||||
Weight | The importance of an object in relation to a set of objects to which it belongs; a numerical coefficient attached to an observation, frequently by multiplication, in order that it shall assume a desired degree of importance in a function of all the observations of the set. The statistical weight is the inverse of the inclusion probability. While this term has many meanings, for Monitoring Resources, we use it in statistical sense. (Source: OECD). |
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Links to useful definitions: