Watershed Restoration Planning

Information System—Final Report

Submitted by Vicki Watson and Christine Brick, University of Montana

To: Clark Fork Natural Resource Damage Program

May, 2002

Project Abstract--The goal of this project was to lay the foundation for a cost-effective information database that would assist restoration project planners and citizens in the Upper Clark Fork River Basin in their efforts to identify and evaluate restoration opportunities, priorities and outcomes.  Our project built on the efforts of the Montana State Library’s Natural Resources Information System (NRIS) to develop an online, interactive, map-based clearinghouse of water-related information.  The Upper Clark Fork Basin has more information than most watersheds, and has special concerns with respect to large-scale mining and smelting remediation and restoration.  We have attempted to identify critical information needs, describe and evaluate available information sources,  identify information gaps, and propose a method of delivering information to users that also stimulates the development of new information. A model for that system is presented online, and we hope that a similar system could be housed with NRIS, which is the entity most capable of maintaining such a system and providing the technical services required for its effective use. We recommend that NRDP contract with NRIS to maintain and service such a system. Our findings and recommendations are our responsibility and do not necessarily reflect the opinion of the NRDP on these matters. 


The science of watershed restoration is a young science, struggling with tasks and expectations that would challenge a much older science. Yet our best opportunity to push this science forward and to speed recovery of damaged watersheds is to undertake restoration projects and learn as we go. Hopefully, through careful planning, based on the best available information, and rigorous analysis of the outcomes of our efforts, we will do more good than harm, and our efforts will improve with time. This is the approach of the Clark Fork Natural Resource Damage Program. To guide its restoration planning effort, the NRDP seeks to develop an information system that delivers relevant available information to a wide variety of users and that also stimulates the development of new information.

To assist the NRDP with this effort, we undertook a project with the following objectives:

  • Identify key types of information useful in watershed restoration planning
  • Identify, evaluate and describe relevant available information
  • Identify key information gaps  
  • Consult with potential users of this information on how best to deliver the information to them
  • Consult with NRIS on how to deliver this information
  • Recommend a system to deliver available information and to stimulate filling of gaps

This report summarizes our findings and recommendations for each of these objectives.

Identify Key Information Needed for Watershed Restoration Planning:  

**Note:  Much of the discussion in this section was developed by Watson for a course in Watershed Conservation Ecology at the University of Montana.  The discussion was adapted to fit the objectives of this project.

Watershed restoration planning must take place in the context of general watershed conservation planning—otherwise restoration efforts can be undone by other actions occurring in the watershed. Hence the information needs of restoration planning are essentially the same as the information needs of watershed conservation planning.  The information needed for watershed planning can be best described by looking at the steps of the planning process. Planning steps include:

  • Develop watershed goals and objectives

  • Identify problems, present and future

  • Analyze causes of problems

  • Recognize conflicts but seek common ground

  • Select action strategy and tactics to reduce problems and conflicts

  • Implement actions; track outcomes; rethink earlier steps

Each of these steps requires a variety of types of information. Some key questions associated with each of these steps will help to illustrate some of those information needs.

Develop watershed goals that unify and clarify values—Citizens and planners ask:   What do we want to sustain and what do we want to change? What are key watershed services, resource uses and values we want to restore and maintain? What is the desired condition of the watershed and its various parts? Do we seek restoration of full ecological potential? Or reclamation that will support human uses? Or remediation that will meet health, safety and environmental standards?  Or just fewer conflicts between users? Or some combination? What is our desired time frame for achieving these goals and objectives?

Answers to the above questions require information about watershed services, resource uses, relevant legal standards, and the system’s ecological and restoration potential (as defined by relevant reference systems or historical data). With such information, citizens can better translate broad watershed goals into objectives that are the SMARTEST-- Specific, Measurable, Achievable, Respectful, Tractable, Ecological, Sustainable and eThical.  

  • Specific – specific to the area and its problems, and clear and unambiguous;

  • Measurable – can be measured meaningfully and with reasonable accuracy & precision;

  • Achievable – technically and economically feasible;

  • Respectful – respectful of the concerns of all stakeholders;

  • Tractable – under the control of those involved in the planning process;

  • Ecological – considers ecological constraints and concerns;

  • Sustainable can be sustained ecologically, economically, politically;

  • Ethical  – considers the needs of those with little power, including future generations

At each step in the planning process, citizens will need to seek advice of relevant technical advisors – Are our goals/objectives realistic (given the system’s natural limits)? What is normal and possible for this area? Are our goals mutually compatible? Is our time frame for recovery realistic?  

Identify problems, past and future—Citizens ask themselves and their technical advisors: Where do we stand in meeting our goals/objectives? What is the current condition of the system? Is it supporting beneficial uses and providing desired services and values? Is it able to sustain itself? What appear to be the trends in its condition (getting worse? better?) What user conflicts exist now? Given expected trends in population and development in the area, what new conflicts or growing conflicts seem likely?

Analyze the system and causes of problem—Citizens ask their technical advisors: How does this system (watershed) work? What processes shape the kind of system it can be (classify it) and its condition/health/integrity? What are the probable causes of the problems we have identified? What actions seem to have the greatest potential to reduce these problems without causing other problems? To answer these questions, the technical advisors will need to consider the nature of the particular system (its classification), the connections within and between ecosystems, natural and human causes of change, and the capacity of the system for providing goods and services and absorbing stress.

Recognize conflicts but seek common ground—Conflict is almost inevitable in efforts to restore damaged ecosystems. By the time restoration efforts are begun, ecosystems are usually damaged by a variety of uses, and all those uses will likely need to make changes to allow the ecosystem to recover. No one wants to incur costs or make changes unless they are sure the efforts are necessary and likely to be successful and that all interests are doing their part. An information system that generates and delivers relevant information should reduce some of the uncertainty that stimulates conflict. In addition, it can be used to store information about restoration projects that allow all to see the efforts being pursued by others.

Select action strategy and tactics to reduce problems and conflicts—Because watersheds are highly connected, actions in one area can have unintended consequences on other areas. Narrowly focused efforts to address a problem can shift the problem elsewhere or create new problems. For example, stabilizing banks with riprap degrades habitat and can worsen bank erosion downstream. Heavy fertilization to encourage revegetation can create excess nutrient loading to streams. Use of non-native plants in revegetation can produce weed problems. Increasingly, restoration specialists recognize that an overall restoration strategy that strives to understand and work with natural processes is more cost-effective in the long run than strategies that work against natural processes. Identifying those natural processes requires information such as natural flow regimes (and associated natural temperature and sediment regimes), floodplains and meander zones, erosion rates, and native plant communities.

While a community may wish to restore certain aspects of a watershed damaged by human uses, frequently many historical changes in the watershed are considered desirable or at least necessary to achieve safety or economic goals. Hence the community must determine what is to be preserved, what is to be conserved and what is to be restored? That is, which areas or processes need to be kept largely natural in order to restore and sustain the ‘health’ of the stream and its watershed and resources associated with these? Which areas or processes can be altered so as to achieve other human purposes (and what is the limit to change that can be tolerated without harming the system and other users)? Which areas and processes have been so damaged, depleted or otherwise altered that we need to change our practices and allow recovery or even carry out an aggressive set of restoration actions? Once these areas and processes have been identified, planners can begin to identify which are likely to be most cost-effective, which should be pursued first, etc. An information system could identify and map critical preservation areas (water bodies, wetlands, riparian areas, floodplains, meander zones, key habitat, etc) as well as degraded areas (dewatered streams, contaminated floodplains, etc).

Implement actions; track outcomes; rethink earlier steps The purpose of planning is to act. An information system can track what actions have been taken, by whom, where, when, at what cost. It can also track outcomes (i.e., store monitoring information and evaluations of that information). Post-project monitoring is critical for evaluating the relative success or failure of the project itself, but it can also be used to evaluate participant's perceptions of the project and the process.   Such information is essential to allowing citizens and planners to rethink goals/objectives, the nature and causes of problems, and the effectiveness of their strategies and actions.

Types of Watershed Information

No doubt the reader is thinking – "Enough already with talking about the kinds of information needed in watershed planning. Just tell me where I can find the data I need to make decisions."   Unfortunately, raw data will provide citizens and planners with very little help in making decisions about watershed restoration. It is important to realize that raw measurements may require a lot of synthesis and interpretation before they become useable information. For example, the U.S. Geological Survey provides daily stream flow data, but this alone doesn't tell us what we really need to know for channel restoration, namely, how often can we expect either low flows or floods of a given magnitude. For this, the raw stream flow data must be plotted as flow duration curves or as recurrence interval plots.  Watershed decisions may require some very complex information that is seldom generated on a routine basis for large areas.  

Watershed information exists at several levels of interpretation. There is information gained by fairly direct observation/measurement at specific points and times  (such as elevation, soil texture, stream flow, fish counts, etc). Such raw data are collected by various resource specialists  (soil scientists, hydrologists, biologists, etc) who analyze and interpolate it over space and time to produce maps of topography, soil type, land cover, groundwater depth, seasonal flows, or fish distribution for example. Several kinds of information can be synthesized or integrated to identify areas that have a higher potential or risk for some phenomenon of interest (like erosion risk, groundwater contamination risk,  fishery recovery potential, etc). Watershed scientists also use a variety of information types and complex models to classify watersheds and water bodies, to describe their condition, connections, capacities, changes, and causes of problems.  Development of watershed indicators of condition, capacity, etc. is a critical need, and one that we are currently pursuing. Finally, all these types of scientifically derived information must be evaluated to determine which areas are higher priorities for restoration, preservation or conservation practices. Determining that an area has a higher priority for an action or is less suitable for a particular type of land use is a value judgment. Such decisions are informed by scientific information, but must ultimately be made based on values. Table 1 shows more examples of these several levels of information and interpretation.

Identify, Evaluate and Describe Relevant Available Information

With the above in mind, we compiled a list of information potentially useful to watershed restoration decisions. The list includes information types that range from raw data to highly interpreted information and is organized by subject into sections covering climate, land forms and geology, soils, land cover and vegetation, water (surface and ground), fisheries, human systems, known and potential threats to water resources, and efforts to restore and conserve water resources. This is a working list that will never be finished because watershed science continues to advance and information about the basin will continue to evolve over time. (The list is currently available here.)

In addition, as the list of relevant information was being compiled, specific sources of information were sought out and evaluated. Many government agencies collect data and generate information useful to watershed planning. Some of that information is stored in databases or information systems, some of which are now available online. The following key databases and information systems were evaluated and described (click on link to view description):

In addition a number of information sources were briefly described under specific information types, including: Western Regional Climatic Center, NRIS’s drought information site, UM Watershed Health Clinic algae database, and lists of relevant theses. The Clark Fork Database Management System is described on under the section on ‘known/potential threats’ but does not appear in the list of key databases since it was judged to be of limited usefulness.

The descriptions of these databases and information sources attempted to provide the following information to the extent possible:

  •      Purpose and nature of database/information system
  •      Location of sample sites/areas assessed  and nature of location info in database
  •      Time frame – duration and frequency of sampling; frequency of updating of database
  •      Parameters measured and methods used
  •      Quality of data and degree of documentation – suitability for various uses
  •      Relevant references
  •      Responsible party contact info (person/position, agency/affiliation, address)
  •      Website if available online
  •      Usefulness to restoration planning
  •      Recommendations for making the info more useful  

Identify Information Gaps

Information considered useful to watershed restoration planning, but could not be located in the sources surveyed, is listed on the web site under the same categories as the available information. Brief descriptions of this information and its potential usefulness appear on the website under Information Gaps. It is hoped that these descriptions will stimulate the development of this missing information. In addition, if the information does exist, it is hoped that those using the web site will inform those responsible for maintaining the web site of the location of that information.

Some types of information that would be especially useful to current restoration planning efforts: detailed maps of irrigation systems, location of high quality wildlife habitat in need of protection, stream morphology and riparian condition of tributaries.

Some types of information that would be useful once the Superfund work on the main stem is complete would be: post reclamation metal contamination levels in stream bed, banks and floodplain of the main stem;  post reclamation stream bank morphology and extent of vegetative cover; nature and location of any stream bank stabilization that was installed. 

Consult with potential users and deliverers of this information on how best to deliver the information

We informally surveyed conservation districts, watershed groups and natural resource professionals in the upper Clark Fork basin to determine their information interests as well as their information technology constraints. In addition, we consulted with NRIS personnel concerning their thoughts and constraints on providing such information. We also organized two workshops in collaboration with NRIS personnel to demonstrate NRIS’s current capabilities for delivering watershed related information and to discuss with potential user groups their information needs and preferences on information delivery options.

We found that potential users almost universally had access to the internet but had a very wide range of sophistication in the use of information technology. Some users preferred that information be provided as simple static maps, while others preferred to have spatial data that they could manipulate and use to develop their own analyses and interpretations. All the users like the idea of having an online clearinghouse that quickly pointed them to available relevant information and that also provided some indication of how that information could be used. Several of the more sophisticated user groups had their own databases and were interested in integrating those with larger efforts (including  Butte-Silver Bow County, Missoula County Health Department and Office of Planning and Grants, and the Tri-State Water Quality Council). Based on the above interactions with potential users and deliverers of information, we developed the following recommendations. 

Recommend a system to deliver available information and to stimulate filling of gaps

Any information delivery system has to recognize that potential users range from those with minimal information technology skills to those with advanced skills. NRIS’s information clearinghouse recognizes this and provides information in a variety of ways. For the most basic users, there are static maps of key information. For more skilled users, there is NRIS’s online interactive mapper which allows the user to specify an area of interest and then create a map of some desired information (like land use) and overlay this information on a base map of key location information (like roads, towns, county borders, streams). For the most advanced users, all the information available in the above maps can be downloaded for use in a GIS system. In addition, other GIS information is available to download.

In addition to the information available at the NRIS site, the site provides links to still more information available at other web sites. A great deal of basic natural resources information is available at web sites of the USGS, NRCS, etc. The NRIS web site provides links to these, both in the form of simple lists of info types and also in the form of interactive maps. This is a particularly helpful approach that allows the user to select a site on a map, and then access all the various kinds of information available about that site. Often, one of the greatest difficulties in accessing natural resource information is the need to know all the different site identification numbering systems used by many different agencies. This problem is removed by the linked map approach. Simply select the kind of information desired and the area of interest; then, once the map is built, click on the site of interest and you are passed through to the database containing that information, right to the information about the site you selected. 

Information relevant to watershed decisions comes from many scientific disciplines and exists as voluminous raw data and in a variety of more summarized and interpreted forms of information. It would be very difficult for one source to host all this information or to provide it all in a form useful to every kind of user. NRIS is not a major repository of raw data, but prefers to store only the more summarized and interpreted information. As described above, NRIS provides links to the massive databases with specific data on soils, water quality, flows, etc.

Hence the NRIS site already has powerful information clearinghouse abilities and a large amount of relevant information. The main things NRIS needs to meet NRDP’s information needs are some suggestions for how to organize the information for easier reference by a wide variety of users, and funding to maintain and expand the available information.

To meet NRDP’s information needs for restoration planning, we recommend that  NRDP develop a restoration planning web site that contains the following:

  • Planning documents – mission, vision, goals statements, annual plans and reports (we recognize that this currently exists on the NRDP website)

  • List of Stakeholders involved in the planning process and their contact information

  • A database of NRDP projects and related projects organized like the Blackfoot River restoration projects web page:  http://www.r6.fws.gov/pfw/montana/mt5c.htm.   In addition to the information stored on the Blackfoot web page, project plans and reports should be available online. In addition to restoration projects, final reports of 319 and TMDL studies in the area should also be available online since these include information useful to restoration planning.

  • A watershed information clearinghouse modeled on the web page developed by this project.  

NRDP could contract with NRIS to provide all of the above, or just the last two items.  This will be a cost-effective investment for NRDP. We recommend that a mere 1% of NRDP’s planned annual expenditure of $7million (or $70,000) be invested in an information management system that assists planners and citizens  to identify & evaluate restoration opportunities, priorities and outcomes in the upper Clark Fork basin.  In addition, we recommend that 5% of that annual expenditure  (or $350,000) be invested in an assessment & monitoring system that gathers the information to populate that information management system.