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Ecological Management Action Plans


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EM-12 Storm Water Management

EVALUATION METHODS

Components of Plan

The plan promotes the use of alternative methodologies for disposal of storm waters. BTMC will encourage, facilitate, and coordinate such efforts in BTES, and support studies that will increase the knowledge base of various aspects of alternative storm water disposal. Usefulness of the various programs are anticipated in 1) reduced loadings of nutrients, fecal coliform bacteria, and pollutants to BTES water bodies, 2) improved water quality in BTES in support of enhanced natural resources, and 3) enhanced wetland vegetation.

 

Interrelationships Among Components

A database compiled by CLIWS identifies 556 storm water pumps in Barataria and Terrebonne basins. Various components of a database that will support location of projects for alternative management of storm water disposal are yet to be completed. A proposal by the Lafourche Coastal Advisory board for a storm water treatment/wetland enhancement project is pending for funding under CWPPRA. Other demonstration projects are feasible with assistance from local government, state (LDEQ, LDNR) and federal (EPA, NRCS, USACOE) agencies, and CWPPRA. Monitoring of the results of the demonstration and/or actual projects will be conducted by the implementor(s). BTMC would serve as a coordinator of knowledge gained from project results, a translator and disseminator of the knowledge through public education programs, and a facilitator for additional projects.

•. The lead implementor is BTMC and LDEQ [seems that there should be a single lead with collaborators, or a work group of agencies]. Collaborating organizations are LDNR, local government, drainage districts, LDHH, LCES, EPA, NRCS, USACOE.

•. Costs for the initial project will be borne by the sponsoring parties and CWPPRA. Other demonstration projects will be cost shared by the relevant cooperating agencies. Costs of developing an appropriate database, coordinating results from projects, developing and disseminating education programs, and in coordinating efforts will be shared by BTMC, LDEQ, and collaborating agencies.

Documentation of Plan Implementation and Success

Monitoring for this Action Plan includes assessing the timely implementation of the components of the Action Plan, and the eventual success of implementation (i.e., improved water quality and enhanced wetland vegetation). The first component is not conducive to monitoring in the traditional sense of data collection and analysis (e.g., water quality monitoring), but rather a tracking. The monitoring of implementation is designed to determine whether BTMC facilitated the initiation of alternative storm water discharge management methods and whether a better informed public resulted. Monitoring the actual results of the storm water management projects will be conducted by the implementor(s). The focus of the Action Plan should be on monitoring of the individual projects by the implementors and forwarding of that information to BTMC for their incorporation into educational programs, re-examination of issues, re-formulating plans for further projects.

•. Eventual success of the Action Plan may not be identifiable in a basin-wide (or subsegment) analysis of water quality or ecological indicators, because the projects are isolated and may be limited in number, thus reducing an overall, identifiable effect . The success of Action Plans that target reduced sewage pollution, reduced agricultural pollution, and storm water management may all be manifested in similar improvements in water quality and indicators of ecosystem health. If all Action Plans are working in parallel and water quality improves, it will be difficult to determine the cause and effect. Since the scale of implementation will vary among Action Plans, the level of success in improved water quality will also vary. The probability is high that implementation of any single management scenario may have varying effects in different environments. It is also possible that no single indicator may indicate program success, but rather success will be seen in a combination of indicators. The end result of multiple actions to improve water quality, however, will be noticeable in indicators of basinwide ecosystem-level health (see CCMP-Part 4, "Monitoring Plan for Ecological Indicators").

•. Specific steps in the Action Plan that can be tracked and/or indicators of success that can be analyzed for change are proposed below. They can be expanded or modified, should be reviewed periodically, and should be amended as appropriate.

Plan implementation

•. Establish lead and collaborating implementors, secure sources of funding, identify a project work group and respective responsibilities, and develop a detailed time line (months 0-4).

•. Encourage the acceptance of demonstration storm water project by CWPPRA (months 0-12).

•. Identify information needs, formulate studies, secure funding, implement data collection and research projects (months 6-12).

•. Begin development of public education programs (months 6-12).

•. Support studies of:

¨ . storm water discharge constituents,

¨ . characterization of receiving water bodies,

¨ . attributes of wetland areas that are conducive to retention and treatment of pollutant loads without detriment to the wetlands,

¨ . identification of suitable wetland receiving areas, and

¨ . identification of suitable demonstration project sites.

•. Emphasize treatment areas that are known to assimilate dissolved nutrients, e.g., freshwater swamps.

•. Support projects that are designed so as not to lose any more naturally functioning wetland areas.

•. Encourage monitoring for indicators that wetland vegetation and natural processes are not impaired as a result of the project. Any negative effects should also be incorporated into the BTMC educational programs and re-assessment of direction of the Action Plan.

•. Dissemination of educational programs (years 2-10).

•. Coordinate information obtained from various projects (monitoring of success by various implementors) and incorporate into educational programs (years 2-10).

•. Coordinate information obtained from various projects (monitoring of success by various implementors) and incorporate into improved management technologies (years 2-10).

•. Encourage other governmental bodies to develop alternative storm water management practices and projects (years 2-10).

•. Continue encouragement of other demonstration projects (years 2-10).

Project success

•. Individual storm water management projects will be monitored by the implementor(s).

•. Establishment of sample design for specific targeted study areas.

•. Establishment of baseline data for specific targeted study areas.

•. Monitor appropriate parameters that indicate the amount of pollution from storm water discharge that affects the system is reduced.

•. Water in relevant BTES subsegments meets all state/federal guidelines; no impairments due to storm water discharges.

•. Data analysis to determine success of the various projects. Effects are anticipated in

¨ . reduced loadings of nutrients, fecal coliform bacteria, and pollutants to BTES water bodies,

¨ . improved water quality in relevant BTES watersheds or subsegments in support of enhanced natural resources,

¨ . enhanced wetland vegetation, and

¨ . improvement in ecological indicators.

Methods

Measurable parameters

Plan Implementation - The activities of various agencies outlined above in implementing the plan will be monitored for indicators such as:

•. Lafourche storm water disposal/wetland enhancement project is implemented under CWPPRA.

•. Plan for tracking progress of Lafourche project is developed and implemented.

•. Plan for educational programs and their dissemination is established.

•. Plan for encouraging other storm water management projects is developed.

•. List of data needs and types of studies identified, outlined, and funding secured.

•. Enumeration and description of studies initiated, tracked, and completed.

•. Incorporation of knowledge from completed studies in expanded educational programs and improved management technologies.

•. Increased public education programs concerning storm water discharge pollution problems and alternative management strategies.

•. Increased number of alternative storm water management projects.

Project Success

•. Decreased evidence of storm water pollutants in specific targeted study areas.

•. Decreased evidence of storm water pollutants as cause of impairment of water bodies in specific targeted study areas.

•. Increased evidence of wetland vegetation enhancement at alternative storm water management sites.

•. Improvement in ecological indicators that would indicate a reduction in storm water pollution.

Data collection methods

Plan Implementation - The monitor will contact the various agencies involved in the implementation to gather data (examples below) that will be incorporated into a monitoring report:

•. Check-off system according to time line of project as landmark dates are encountered and project objectives are met.

•. Person-months of involvement of various agency personnel are documented by the implementor and collaborating agencies.

•. Tracking of time line, implementation, monitoring results of various storm water projects.

•. List and descriptions of educational programs developed.

•. List of recipients of educational programs, including dates, types of programs, and comments made by recipients of educational programs as to usefulness of the program.

•. Lists, descriptions, and results of alternative storm water management projects are maintained for review by cooperating agencies and BTMC.

Project Success

•. Reports of results of alternative storm water management on water quality of adjacent receiving water body. Provided by implementor(s) of project. Summarized by monitor for incorporation in reports.

•. Reports of results of alterations of wetland habitat at receiving end of altered storm water discharge systems. Provided by implementor(s) of project. Summarized by monitor for incorporation in reports.

•. Monitoring of individual projects incorporates

¨ . establishment of baseline data,

¨ . routine water quality monitoring and agricultural pollutant monitoring as established in state and federal agencies,

¨ . designations of degraded water quality (i.e., not meeting or partially meeting designated use due to storm water pollutant sources),

¨ . parameters for assessment of storm water pollution effects,

¨ . indicators of wetland condition, wetland vegetation enhancement, and

¨ . ecological indicators such as chlorophyll biomass, phytoplankton composition, noxious algal blooms, nutrient levels, BOD, fish kills due to pesticide runoff, fish kills due to herbicide applications, water clarity.

Much routine baseline information exists, e.g., LDEQ Water Quality Inventory, various data sets analyzed for "Status and Trends of Eutrophication, Pathogen Contamination, and Toxic Substances in the Barataria-Terrebonne Estuarine System" (Rabalais et al. 1995), "Status and Trends of Hydrologic Modification, Sediment Availability and Habitat Loss/Modification in the Barataria-Terrebonne Estuarine System" (Reed, ed., 1995) and types of data in the EPA EMAP database, EMAP Wetlands database. Routine monitoring that might indicate the amount of storm water pollution affecting the system includes nutrients, pesticides in water, sediment loads, salts, fecal coliform levels, BOD, dissolved oxygen, insecticide- or herbicide-related fish kills. Other baseline information is missing, e.g., system-wide analysis of DO, nutrients, phytoplankton composition and biomass, benthic indicators, storm water discharge-source pollutants in water, sediment and biota, indicators of biotic integrity and ecosystem-level health.

Sample design and statistical methods

Plan Implementation - There are no relevant sample designs or statistical analyses for the evaluation of plan implementation.

Project Success - Long-term data sets of routine water quality monitoring data that might indicate a change in water quality over time are applicable to nonparametric trend analysis techniques (e.g., modified Mann-Kendall tau tests and seasonal Kendall slope estimator tests; see Hirsch et al. 1982). Tests similar to those used in "Status and Trends of Eutrophication, Pathogen Contamination, and Toxic Substances in the Barataria-Terrebonne Estuarine System" (Rabalais et al. 1995) would be appropriate for the routinely collected water quality monitoring data. Within any single storm water management project, appropriate statistical techniques can be applied to test for differences in receiving water, wetland vegetation, etc. as a result of implementation of the project. Initiation, completion, and subsequent altered storm water disposal techniques will be implemented on a varying time schedule and not distributed uniformly throughout BTES. A system-wide analysis of effects is not appropriate.

Cost estimates

Estimate one-half person-month per year for monitoring all the aspects of Action Plan implementation and the cooperative efforts of each agency. Including salary, fringe, incidental costs, and indirect costs = $4,000 for each year (no inflation). Modifications in monitoring plan (see below) should result in modifications of cost. Additional costs of monitoring storm water discharge studies will be borne by implementor and collaborating agencies.

Implementation of Monitoring

Monitor

Since BTMC is the proposed implementor for this Action Plan, an outside monitor not selected directly by BTMC is desirable. The combined work group of representatives of the cooperating agencies should agree to an outside monitor who will then be contracted by BTNEP. A monitor will prepare reports to be submitted to BTMC. Although individuals involved in the implementation of the Action Plan may prefer a team member to monitor the project, usually a Third Party offers the best option as the responsible individual for the monitoring. Independent reviewers should be free of vested interests, historic commitments, unrestrained by mission statements, and free from personnel or budgetary actions. The implementor and cooperating agencies will provide the project monitor with data products listed above for subsequent assessment of accuracy and incorporation into reports. The monitor should interact directly with each cooperating agency to determine their level of commitment and activities for the various reports. Success of the monitoring strategy depends on the commitment of participating agencies and individuals to make monitoring an integral part of the CCMP and to provide the Action Plan monitor with the data required to develop reports to BTMC.

Reporting schedule

The monitor will prepare quarterly reports. Reports will be submitted not less than 15 days prior to a regularly scheduled meeting of the BTMC. The party responsible for the monitoring should be available to discuss the report at the meeting if requested to do so by the BTMC. Monitoring reports will also be provided to the agencies or institutions participating in implementation. Interim reports can be prepared by the monitor at any time to draw BTMC attention to significant problems, delays, etc.

Guidance for monitoring reports

•. Quarterly reports to BTMC shall provide suitable components, such as:

¨ . Check-off of project landmarks according to the project time line.

¨ . Assessment of cooperating agency contributions.

¨ . Description of educational programs.

¨ . Compilation of recipients of educational programs and their comments.

¨ . Compilation of storm water management projects initiated, completed, and in progress.

¨ . Compilation of results from storm water management projects.

•. Technical details may be included in the report, in a presentation suitable for the Scientific Technical Committee and/or BTMC. A summary of the report shall be less than one page and be suitable for presentation to and understanding by the general public.

•. In addition to the evaluation of the technical accomplishments of the project, the monitor shall

¨ . identify problems observed during the reporting period and their potential causes;

¨ . predict the short- and long-term consequences of the problems;

¨ . recommend actions to address the problems, as well as a potential implementor(s);

¨ . identify a time frame for accomplishment of the recommendations.

Review of monitoring reports

The BTMC shall receive the quarterly reports. The BTMC shall discuss the monitoring document and take actions it feels appropriate with regard to the implementation of the Action Plan.

Modification of monitoring plan

BTMC may at the end of any annual cycle change the periodicity or components of the monitoring reports if it feels the frequency or components of reports are inappropriate to keep abreast of the project. Changes in the independent reviewer can be made after any annual cycle, but only with the knowledge and participation of the work group of cooperating agencies, the independent reviewer, and BTMC.

QA/QC

Quality assurance/quality control in the usual sense of precision and reliability of data collection does not apply to most of the monitoring plan for this Action Plan, since the monitor is tracking the development and implementation of a series of programs and regulations. Certain features of quality assurance, however, can be applied to aspects of the monitoring plan:

•. Collection of information in an objective and systematic manner.

•. Use of qualified and experienced personnel.

¨ . Independent Third Party with no vested interest, not a BTNEP employee.

¨ . Chosen by work group of cooperating agencies in collaboration with BTMC.

¨ . Knowledgeable about storm water pollution issues, educational and demonstration projects, water quality monitoring programs and databases, wetland ecology.

•. Application of standard formats for quarterly reports.

•. Maintenance of a quarterly schedule.

•. Consistent and timely review of monitoring reports by BTMC.

References

Hirsch, R M., J.R. Slack and R.A. Smith. 1982. Techniques of trend analysis for monthly water quality data. Water Resources Research 18: 107-121.

Rabalais, N.N., Q. Dortch, D. Justic, M.B. Kilgen, P.L. Klerks, P.H. Templet, R.E. Turner, B. Cole, D. Duet, M. Beacham, S. Lentz, M. Parsons, S. Rabalais, and R. Robichaux. 1995. Status and Trends of Eutrophication, Pathogen Contamination, and Toxic Substances in the Barataria and Terrebonne Estuarine System. BTNEP Publication #22. Thibodaux, LA: Barataria-Terrebonne National Estuary Program.

Reed, D.J. (ed.). 1995. Status and Trends of Hydrologic Modification, Sediment Availability, and Habitat Loss/Modification in the Barataria-Terrebonne Estuarine System. BTNEP Publication #20. Thibodaux, LA: Barataria-Terrebonne National Estuary program.

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