Example - Stream Monitoring

Step 1 Set Goal & Scope

Regional Monitoring Networks (RMNs; U.S. EPA 2016) are collaborative efforts between the U.S. Environmental Protection Agency (U.S. EPA) and states, tribes, and other entities to collect long-term regional data with consistent methods. Goals include documenting current conditions, tracking changes at regional scales over time, and documenting whether changes are associated with changing thermal and hydrologic conditions (Figure 1).

Timeline showing ways data can be used over different timeframes. — *Figure 1. RMN data can be used for multiple purposes, over short- and long-term timeframes.*

Map showing locations of active stream RMN sampling sites. — *Figure 2. As of February 2023, there were 80 active stream RMN sampling sites in the eastern and midwestern U.S. Background colors indicate EPA Level III ecoregions.*

The scope includes all states and monitoring entities in the U.S. that want to participate. Data from the RMN sites are pooled to enable more robust analyses and allow the detection of the widespread climate-related patterns that may otherwise be missed at the local level. Active stream RMNs exist in the Northeast, Mid-Atlantic, Southeast, and Midwestern U.S. regions (Figure 2). The aim is to achieve nationwide coverage. The geographic boundaries of the RMNs typically align with U.S. EPA regions because states and tribes are the main participants at this time, and the U.S. EPA regional offices facilitate coordination and sharing of resources.

Step 2 Assess Threats & Vulnerabilities

Assessments of threats and vulnerabilities (not limited to climate change) have been considered to varying degrees for evaluation and prioritization of sites (Step 3) for inclusion in RMNs, as well as for indicator selection (Step 6). During the development of the Northeast RMN, sites were assigned to overall climate change vulnerability categories based on projected changes in temperature and hydrology (exposures) in combination with sensitivity factors such as shading and baseflow (Figure 3). In addition, the RMNs are helping partners build the capacity to better monitor threats and vulnerabilities by collecting high-frequency sensor data (U.S. EPA 2014). The sensors allow partners to document extreme thermal and hydrologic events' magnitude, frequency and duration and track whether changes are occurring as projected.

Schematic of the exposure and sensitivity variables that were considered in the vulnerability assessment. — *Figure 3. Components of the vulnerability assessment that helped inform site selection in the Northeast stream RMN.*

Step 3 Identify, Evaluate & Prioritize Site(s)

A river running through a forest. — *Figure 4. Example of a high quality ('reference') site.*

During the initial phase of establishing RMNs, high quality sites (with low levels of anthropogenic disturbance and low potential for future development; Figure 4) were identified because they are the benchmarks against which other sites are compared. In the absence of other stressors at high quality sites, there is a higher likelihood of detecting climate-related changes.

Other factors are considered for RMN site identification, particularly in places where minimally disturbed sites are rare or absent. Results of vulnerability assessments have been considered to varying degrees for site evaluation and consideration during the prioritization of sites for inclusion in the RMN. In 2012, the Northeast partners selected stream RMN sites in the 'moderate' to 'most' vulnerable categories (see Step 2).

Due to limited funding for RMN implementation, practical considerations are also weighed. For example, the additional value of a site with a lengthy historical record that is part of existing monitoring networks or has existing equipment, such as a U.S. Geological Survey gage, may be considered even if the site has a higher-than-desired level of disturbance. Accessibility, land ownership, and opportunities for partnership or collaboration are also important considerations.

Step 4 Identify, Design & Select Interventions

High-quality sites were targeted during phase one of the RMNs. While they are low priorities for restoration interventions, some sites are good candidates for protection planning.

Map showing percentages of cold water macroinvertebrate taxa in different stream locations. — *Figure 5. Percentages of cold water macroinvertebrate taxa are being tracked at RMN sites.*

Protection planning priorities were incorporated into the 2016 Clean Water Act reporting cycle and may also be used for other EPA programs, such as the EPA Healthy Watersheds Program. While some RMN sites may have existing protections, protection planning at a regional scale has not been formally pursued. Developing strategies to help practitioners better protect high-quality sites, especially those with cold water habitats (Figure 5), will be an important future development area.

Step 5 Assemble Objectives, Targets & Action Plan

Cover of the Stream RMN report. — *Figure 6. Cover page of the Stream RMN report.*

While the RMNs do not have action plans for interventions, they have reports documenting their development (Figure 6), protocol documents, and Quality Assurance Project Plans (QAPPs) that serve as action plans for implementation and achieving data quality objectives. RMN partners strive to use consistent and comparable methods whenever possible, as different methodologies may introduce biases in analyses and contribute to variability, which reduces the sensitivity of indicators and increases trend detection times.

Step 6 Implement Interventions & Monitoring

A biologist sampling stream macroinvertebrates with a net.

Although interventions are not being developed at RMN sites at this time, in some cases, the indicators and protocols being monitored at RMN sites may be useful for tracking effectiveness of interventions of other projects. In addition, data from high-quality RMN sites could potentially be used to help set realistic restoration targets given climate change.

Step 7 Document Progress & Evaluate Success

A stream to be sampled for macroinvertebrates.

Interventions are not necessarily implemented at specific RMN sites; however, in some cases, the indicators, protocols, and reference site data from RMNs may be useful for documenting progress and evaluating the success of other projects.

For judging the progress and success of the RMNs, measures of success include:

Are data quality objectives being met?
Are RMN data being applied and integrated into Clean Water Act programs to their fullest potential?