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1975 EPA Study Extensive construction in 1950s -1970s Poor canal flushing results in “stagnation, putrification, and excessive nutrient enrichment in water column” Canals > 4 -5’ deep violated O2 criteria Septic tanks leach untreated wastewater into canals and nearshore waters Water quality decreased inward of canal mouth
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RECOMMENDATIONS FROM THE STUDY No canal development in wetland areas As part of the permitting process, designate a person responsible for maintenance of water quality standards Canal depths should not be governed by fill requirements (no deeper than 6 feet) Remove septic tanks, implement centralized wastewater treatment Development patterns should be designed with swales to minimize runoff (stormwater) Canal design: eliminate sills, orientation should be considered when designing canals, eliminate dead-in features
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FKNMS Water Quality Protection Program Included in the FKNMS Act 1990/1992 recommend corrective actions and compliance schedules to address point and nonpoint pollution to restore and maintain the chemical, physical, and biological integrity of the Sanctuary, including restoration and maintenance of a balanced, indigenous population of corals, shellfish, fish and wildlife, and recreational activities in and on the water Called for: adoption of WQS; adoption of enforceable pollution control measures (including WQ base effluent limits and BMPs); development of comprehensive monitoring programs; public participation; and identification of funding
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Water Quality Concerns in the Florida Keys: Sources, Effects and Solutions, EPA, 1999, Dr. Bill Kruczynski The water column of many canals over six feet deep is stratified and bottom waters are usually in violation of Florida's Class 3 Surface Water Quality Standard (WQS) for dissolved oxygen. Because they usually violate Class 3 WQSs, canals were excluded from the Outstanding Florida Waters designation in 1985 Canal systems and basins with poor water quality are a potential source of nutrients and other contaminants to nearshore waters Seagrass beds located near the mouths of some degraded canal systems exhibit signs of eutrophication, such as increased epiphyte load and growth of benthic algae nearshore waters. Canal water quality was not considered for the carrying capacity model despite the fact that “canal water quality is an important issue for near-shore environments and is a major public concern” FKCCS, 2002
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Florida Keys Condition Report 2011 Transport of nutrients from canals pose a threat to seagrass and reef communities Water quality in most residential canals is poor when compared to nearshore and oceanic, thus swimming in residential canal water may pose risks to human health Hydrogen sulfide gas is toxic and residences near heavily polluted canals may be at risk. NOAA, 2011
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Florida Keys Reasonable Assurance Document (FKRAD), 2008 A regulatory alternative to Total Maximum Daily Loads (TMDLs) On a case-by-case basis, EPA may allow the State to exclude listing a known waterbody on their 303(d) list based on ongoing restoration activities Monroe County/local stakeholders approached EPA with a proposal to develop a plan to address water quality issues in the Keys Developed a plan (FKRAD) in 2008 that focused primarily on wastewater and stormwater pollution control measures It was recognized at the time that these measures alone would not fully restore canals (ten canals were modeled to evaluate nutrient reductions) Approved by the State in 2012 and subsequently accepted by EPA Revised in 2011 - acknowledged that some canals may not achieve Class 3 DO standards after completion of wastewater projects
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What is a Reasonable Assurance Document? (1) problem statement – low oxygen and excessive nutrients in nearshore/canal waters (2) description of pollution controls/management activities to achieve water quality standards – pollution control measures focused on wastewater and stormwater improvements (3) an estimate of time when WQS will be met – 2020 (4) schedule for implementing pollution controls – 2015 (5) monitoring plan to track effectiveness of pollution controls and report progress – State and WQPP monitoring (6) A commitment to revise the implementation strategy and pollution controls if progress towards meeting WQS is not being shown – adaptive management
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What constitutes acceptable “pollution control requirements”? Because of specific nature of water quality impairments, determinations are case- by-case Evaluate commitment by local/state authority to implement necessary controls Availability of funding for implementation Implementation in a “reasonable period of time” “reasonable”- depends on severity of impairment, size and complexity, technology availability, funding... EPA acknowledges that the level of rigor necessary will vary depending on the complexity of the water quality impairments and corresponding implementation strategies
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TMDL Considerations (Chesapeake Bay example) TMDL is State/EPA driven Federal agencies determine and assign milestone/timelines Identifies all pollution sources and assigns reduction numbers to regulated point and non-regulated nonpoint sources Expand coverage of NPDES permits to sources that are currently unregulated Increase oversight of state-issued NPDES permits Require additional pollution reductions from federally regulated sources/point sources Increase federal enforcement and compliance Prohibiting new or expanded pollution discharges Conditioning or redirecting EPA grants Revising water quality standards Discounting “progress” if jurisdiction cannot verify proper installation and management of controls
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Recommendations Update/revise the RAD to include a plan to implement canal restoration projects Implement corrective actions/water quality improvement projects at the local level. Local government establishes goals/targets/funding/timelines Explore and identify state-of-the-art technologies to bring canals back into compliance with water quality criteria Additional monitoring for canal systems
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