Dear Reader/editor, On behalf of the Taiya Inlet Watershed Council, I would like to thank you for taking the time to read through this document, comment, and edit it. The final product will be a manual for the community to use as a guide to reduce stormwater pollution to Pullen Creek, so it’s important that the definition of stormwater pollution and its sources are clearly stated in the manual. It is also very important that the community have input, since we are a community-based organization. Please feel free to mark this up, tell me what isn’t clear, suggest changes, etc. You can then email it back to me taiyawatershed@gmail.com or you can stop by the watershed office just east of 7th and Broadway. This manual must be finished by July 20, 2012 so please consider that. Sincerely, Rachel Ford 1 Section 1. Introduction The development of this manual was a cooperative effort that relied on energies at the local and state levels. It was funded with monies from the Alaska Clean Water Action (ACWA) grant program through the Alaska Department of Environmental Conservation (ADEC) managed by the Taiya Inlet Watershed Council (TIWC) in Skagway, Alaska. Support and interviews with members of the Skagway community, the Municipality of Skagway, the Skagway Traditional Council, Alaska Power & Telephone, and White Pass and Yukon Route Railroad were all very valuable in the process of producing this document. Special thanks to… Goal The goal of this manual is to inform developers, the Municipality of Skagway, and Skagway residents to promote educated decisions about actions that can help improve water quality in Pullen Creek. The Best Management Practices (BMPs) listed in this manual are such actions that the community of Skagway can take at the residential, business, and Municipal levels to reduce stormwater pollution. Also included is information about permits required for construction and industrial activities in regards to stormwater management. 1.1 What this manual addresses Stormwater is a source of non-point source pollution, so termed because the pollution occurs over a large area from many different origins. Vehicles, people, construction, residential areas, and industry all contribute to pollution in urban streams and rivers. Pollutants present in stormwater may include sediment, metal, and debris that collect on streets, sidewalks, and parking lots and are flushed into rivers via stormwater systems during rain and snowmelt events. Many cities have created stormwater mitigation programs and manuals to reduce the impact of these pollutants on waterbodies. In some cities, stormwater mitigation actions are mandatory and require documentation, in other communities, stormwater manuals give suggestions for concerned citizens to implement on a voluntary basis. Skagway, though small, is not removed from the urban problem of stormwater pollution. Tourism traffic in Skagway during the summer months has the potential to create a large impact on the environmental health of its local waters. Skagway’s Pullen Creek is especially vulnerable because of its proximity to urban activities and its small size. Toxic pollutants accumulate on Skagway’s streets and travel to the water through the city stormwater system and into the creek. In some cases, this water is filtered through an oilwater separator, in most cases however, stormwater runs directly into Pullen Creek or the Skagway River. 2 This manual will describe ways to reduce stormwater pollutants in the Taiya Inlet Watershed by decreasing the amount of pollutants on impermeable surfaces and increasing areas that capture polluted stormwater. These practices outlined in this manual are presently voluntary; however, future regulations from any level of government could create mandatory implementation. Creating the means to implement these practices now can make it easier for people to exercise them regularly in the future. 1.2 What’s at stake? Stormwater pollution occurs when people actively dump toxic chemicals or other materials down a stormdrain, or when they passively allow pollutants to be washed into a stormdrain with runoff or wash water. Many people are unaware that pollution includes: Water from washing vehicles, tools, and equipment Spills and leaks from automobiles and storage areas Erosion from cleared land Animal wastes The U.S. Environmental Protection Agency 1972 Clean Water Act (CWA) was a response to a public interest in protection of national lakes, rivers, and coastal areas. The CWA requires that states develop water quality standards for each type of water use. In Alaska these uses are established in Title 18, Chapter 70 of the Alaska Administrative Code and are (1) water supply, (2) water recreation, (3) growth and propagation of fish, shellfish, other aquatic life, and wildlife. The standards set with each use limit the amount of pollutant that may be present and/ or discharged into a waterbody. Waterbodies that do not meet the standards for their designated use are placed on the 303(d) list of impaired waterbodies. Recovery from that list requires the generation of a Total Maximum Daily Load document (TMDL), which reports the allowable level of pollutants in a waterbody for compliance with water quality standards as well as possible mitigation steps to reach compliance. Pullen Creek In 1990, Pullen Creek and the Skagway Harbor were jointly listed on Alaska’s Section 303(d) list by the Alaska Department of Environmental Conservation because of metals found in sediments. These sediments contaminants were determined to negatively affect aquatic life that live in and on the creek bottom. In 2004 and 2005, monitoring showed that metals existed in sediments in Pullen Creek, which led to the individual listing of the lower mile of Pullen Creek as an impaired waterbody in 2006. The source of these pollutants is associated with the historic transport of metal-laced ore to the Port of Skagway with uncovered rail and truck transport. Dust from uncovered vehicles was deposited throughout the watershed and are possibly still transported into Pullen Creek via stormwater, exacerbating an already concerning water quality issue. The 2010 TMDL 3 report for the metals cadmium, copper, lead, and zinc identified stormwater as a major source of pollution to Pullen Creek. Skagway Harbor In 1990, when the Skagway Harbor was put on the impaired water bodies list for nonattainment of water quality standards designated for aquatic life, high concentrations of lead, zinc, cadmium, copper, and mercury were found by ADEC in harbor sediments. In 2008, metals were found to be significantly lower and attention was turned to petroleum hydrocarbons as the source of aquatic life impairment. Because the probable source of metal contamination (ore transfer and transport) had ceased, metals in sediments are expected to decline over time. Petroleum products, specifically polycyclic aromatic hydrocarbons (PAHs), however, persist and are therefore likely to have an historical as well as a current origin. A TMDL report was prepared in 2011 for the Skagway Harbor that suggested several potential sources of petroleum that lead to sediment toxicity: Erosion from construction projects, historic and recent surface water spills, Pullen Creek, upland nonpoint sources, NPDES facilities, and harbor and vessel activities including petroleum storage and transfer facilities. According to ADEC’s Division of Spill Prevention and Response, Contaminated Sites Program, 7 sites in the City of Skagway are currently contaminated with petroleum. These are residential, commercial, and industrial sites that still contain pollutants that, through erosion and runoff could be contributing to harbor toxicity. The small boat harbor is not included in the area of concern because testing has shown that it meets water quality standards. 1.3 Federal, State, and Local Regulatory Requirements Water pollution is not just a social concern - it is also illegal. Local, state, and national laws regulate discharges and dumping into US waters. Local regulatory requirements Skagway’s municipal code prohibit littering within the city limits, allowing water contaminated with soaps and other pollutants to run down stormdrains, and leaving vehicle fuel and other oil spills on the streets. These actions are punishable by fines. 4 Table 1. Skagway Ordinances Regarding Pollution Title 8 Health and Safety Chapter 8.02 Litter Control 10 Vehicles and Traffic 8.04 Nuisances 10.04 Language 8.02.020 Litter in Public Places 8.02.030 Sidewalks to be kept free of litter 8.02.050 Vehicle loads causing litter 8.02.060 Sweeping litter into gutters 8.02.070 Municipality’s removal of litter from private property 8.04.040 Polluting water 10.04.020 Spilling oil on streets and sidewalks State and Federal regulatory requirements The Federal Water Pollution Control Act (or the Clean Water Act (CWA)) of 1972 regulates discharges of pollutants into US waters with a permitting system. Each facility that discharges water directly to surface water must obtain a permit that limits quantities and types of substances allowed in the discharge water. Monitoring and reporting programs are required for the permit holder and are meant to ensure that the discharge does not harm water quality or human health. Compliance with the CWA is partially delegated to state programs. The Alaska Pollutant Discharge Elimination System (APDES) handles permits from various facilities that regularly discharge water as a part of their operations such as wastewater treatment plants, mines, construction sites, and fish hatcheries. The APDES Multi-Sector General Permit (MSGP) APDES permits establish conditions and limits for the discharge of pollutants from domestic and industrial sources in Alaska. An MSGP regulates discharges from more than one facility with similar wastewater characteristics in a defined geographical area (which can be statewide). An operator of a facility that meets the eligibility requirements of the MSGP will be authorized to discharge waste after filing a Notice of Intent (NOI) with DEC, so long as all conditions of the permit are met. Additional information can be located at: http://dec.alaska.gov/water/wnpspc/stormwater/Index.htm. The Alaska Construction General Permit regulates construction sites that disturb one or more acres or have small parcels that are part of a larger construction project. This permit includes a Storm Water Pollution Prevention Plan (SWPPP), which outline steps 5 that will be taken to reduce erosion and pollution during the construction process. The DEC website has additional information located at: http://dec.alaska.gov/water/wnpspc/stormwater/sw_construction.htm The Army Corps of Engineers (ACOE) 404 Nationwide Permit was established through Section 404 of the Clean Water Act (CWA) and regulates discharges of dredged and fill materials to U.S. waters. In conjunction with an ACOE permit for discharging dredged and fill materials into U.S. waters, parties must also submit their projects to the ADEC for review. The project is reviewed for compliance with the CWA, Alaska water quality regulations, and other relevant state regulations before it is approved or denied. Stormwater BMPs, like regulatory environmental programs, enhance water quality in communities, but are often implementable on very small scales. Each BMP is part of a larger system of BMPs that, altogether, form an effective water pollution prevention tool. Section 2. Stormwater and Best Management Practices 2.1 What is Stormwater? Stormwater is rain and snowmelt in the form of run-off that travels over impermeable surfaces and collects pollutants, transporting them to streams and creeks via stormdrains (also called catchment basins). In Skagway, these pollutants include metals that have been carried as dust from the operation of the ore terminal as well as many other urban pollutants that collect on the streets. Fluids from vehicles, leaks from stored chemicals, litter, pesticides, fertilizers, and pet waste can all accumulate on impermeable surfaces where they are picked up and flushed through stormdrains or carried as runoff directly into streams. Stormwater pollution has two origins, runoff quantity and pollutants. Runoff Quantity Stormwater runoff increases in volume with respect to the amount of land converted from natural conditions to urban surfaces. Development causes an increase in runoff flow rates and volumes that results in erosion, stream channel widening, and loss of riparian vegetation. Impermeable surfaces in developed areas provide a medium for pollutants to collect and act as a conducting agent for runoff to carry them to streams. Pollutants (King County Manual): Stormwater pollutants come in many forms with many different sources, but share the characteristic of impairing biological processes and natural ecosystem functions. Below is a list of pollutants that affect urban streams and rivers through stormwater systems and a brief description of their sources and impacts. Oils, Greases, and Fuels 6 Oils, greases, and fuels, both petroleum-based and food-related, are found on roads, parking lots, driveways, and storage areas for equipment and food wastes. These pollutants decrease oxygen absorption ability in fish by coating their gills, and clog drainage infrastructure, increasing the cost of maintenance. Metals The most common metals found in stormwater runoff are lead, copper, zinc, and cadmium. Contamination of the water column and stream sediments can decrease the health of fish populations and animals that feed on the bottom of streams. Insects that live in sediments can take up these metals to the detriment of their reproductive cycles. Automobile fallout, paints, industrial sites, and pesticides are the most common sources of metals in stormwater. Sediments (Liu et. al 2008) Many people may have trouble thinking of sediments as a pollutant to streams and rivers; however, excess sediments can smother trout and salmon eggs, reduce the availability of insect habitat, affect spawning areas, and cloud water, which limit both plant growth and fish health. Healthy, productive streams have rocky bottoms with many spaces available that trap oxygen for organism use. Aquatic insects make these spaces their homes during different stages of their lives. Pollutants can bind to sediments, which get washed into lakes and streams, and settle on the bottom. The sources of sediments include construction sites, sand and salt application to icy roads, and dirt from vehicles, parking lots, driveways, and sidewalks. In any case where soil is destabilized, such as the removal of vegetation, or the digging of foundations during construction projects, there will be stormwater pollution consequences if protective measures are not taken. Oxygen-Demanding Substances Organic matter such as plant debris, yard waste, food waste, and certain chemical wastes use dissolved oxygen as they decay or chemically react. This leaves less oxygen for other aquatic plants and animals, resulting in high levels of stress or even death. Salmon and trout populations are both very sensitive to low levels of dissolved oxygen. Nutrients Phosphorus and nitrogen are important for plant processes. An abundance of these nutrients will cause overproduction of algae and other aquatic plants resulting in surface scum, and lowered oxygen levels due to plant decay. Some forms of nitrogen (specifically ammonium) can be toxic to fish in certain environmental conditions. The most well known sources of nutrients are in fertilizers used in lawn care and agriculture. Other sources include animal wastes, septic systems, detergents, road deicing salts, vehicle emissions, eroded soils, and lawn waste such as grass clippings and leaves. Vehicle washing is another large source of pollution associated with transportation. 7 Phosphates in detergents can affect oxygen levels in freshwater. Phosphorus is a limiting agent in freshwater systems: excess amounts of this element from phosphate soaps or fertilizers will cause a dramatic increase in the growth of plants and algae. The breakdown of this plant material by bacteria depletes dissolved oxygen leaving less for other aquatic organisms. With continued biological productivity, the receiving waters becoming increasingly eutrophic, a state where algae begins to dominate the waters and other organisms die off due to low levels of oxygen and reduced water clarity. Toxic Organic Compounds Insecticides, herbicides, fungicides, and rodenticides all are toxic organic compounds and are highly destructive, killing fish and poisoning other aquatic plants, insects, and animals. Fecal Coliform Bacteria Pet waste can have very detrimental effects on water quality through several means. When pet waste is washed into creeks and streams, it adds excess nutrients, leading to algae and plant overgrowth and eutrophication. The pet waste itself will consume oxygen in its decomposition process and can release ammonia to the detriment of aquatic life. Bacterial content is another concern. Several studies have shown that bacteria such as e. coli, which is associated with gastrointestinal illness, binds to sediments and persists in streambeds and lake bottoms (Labelle et. al 1980, Schillinger and Gannon 1985). Stirring up these sediments releases the bacteria into the water, which can lead to ingestion by humans and animals. While pet owners do not always see the effects of their pet waste, it is a detrimental addition to a watershed both in terms of stream health and public health. The University of Wisconsin published a list of diseases and parasites that affect humans through contact with pet waste. These include Campylobacteriosis, a bacterial infection causing diarrhea; Cryptosporidium, a parasite causing diarrhea; toxocariasis, roundworms; and toxoplasmosis, a parasite causing head and muscle aches. 2.2 Existing Stormwater Infrastructure The knowledge base surrounding Pullen Creek, its contaminants, and its sensitivity to stormwater influence has been building over several years. In 2004, the Skagway Traditional Council (STC) established baseline data for metals in and around Pullen Creek. The final report contains data collected from soil and water samples highlighting instances where samples exceeded State of Alaska Standards. In 2006, TIWC published a series of maps showing the location of stormdrains across Skagway, outfalls into Pullen Creek, and where possible, pipes connecting drains to outfalls (see appendix). The mapping process included marking areas where drain and outfall function was impaired due to sediments, leaves, or other debris. The project was an effort to educate residents about stormwater infrastructure and to connect pollution on the streets to pollution in the creek as a precursor to the publication of a stormwater best management practices manual. 8 Currently, according to correspondence with Skagway’s Public Works personnel, stormdrains are maintained by sucking out debris and sediments rather infrequently. Four drains on the northern part of Broadway, at the time of this writing, have oil-water separators completely full of sediments. In June 2012, a TIWC staff member and the director of public works visited a stormdrain and dug out the contents of it (see picture). It was estimated that the last time it had been cleaned was the summer of 2004. In the fall of 2011, a trial stormdrain insert was placed in a drain. Over the winter and spring, it collected this much sediment (still need to find out), and still showed signs of proper functioning. The February 2006 Pullen Creek Action Plan, published by TIWC stressed the importance of implementing systems of best management practices to reduce the impact of urban and shipping activities on Pullen Creek. 2.3 What are Best Management Practices? Best Management Practices (BMPs) are actions implemented in residential, industrial, commercial, and municipal areas that reduce pollution to rivers, streams, and lakes by capturing stormwater runoff and limiting pollutants that collect on impermeable surfaces. Some BMPs are source controls, meaning, they prevent contaminants from coming into contact with stormwater. An example of this is repairing vehicle components to prevent fuel and oil leaks or properly disposal of yard waste. Other BMPs are treatments that remove pollutants from stormwater. An example of this is a riparian buffer, which slows the flow of stormwater near the riparian edge of a stream or creek. A lower flow velocity allows for pollutants to adsorb into soils and plants. Plants roots will take up soluble pollutants (Liu et al. 2008). These practices mitigate the stormwater issues that arise with development of natural areas. A different approach is to design urban infrastructure with stormwater retention in mind. This is known as “low impact development” (LID). Throughout the United States, cities have employed LID to utilize stormwater drainage for the growth of functional landscape features. Choice of materials in development projects can improve infiltration of water rather than contribute to runoff, in effect managing stormwater and pollutants at its source and reducing the impact of development on streams, rivers, lakes, coastal waters, and groundwater (EPA 2007). Some aspects of LID are incorporated into stormwater best management practices. This manual is broken into sections regarding residential, municipal, and industrial BMPs. To make best use of it, each user should consult the section that applies to them and consider implementing the steps described if they recognize that stormwater pollution mitigation would be beneficial. Section 3. Residential 9 Residential actions are often small, conscious decisions that add up to positive changes in environmental health. Many residents in Skagway want Pullen Creek to continue functioning and thriving by supporting Salmon and maintaining its aesthetic qualities. These simple actions can promote a healthy Pullen Creek. 3.1 Vehicles Oils and greases from residential vehicles tend to accumulate on driveways and streets where they can be washed into stormdrains. Check for and fix vehicle leaks regularly Use drip pans to collect liquids during maintenance Dispose of liquids in the proper place: in Skagway, the small boat harbor collects oil, antifreeze, and used car batteries and disposes of these substances without damaging ground or surface water Be prepared to clean up after leaks when they do occur. In many cases, cat litter will soak up liquids and can be disposed of in the garbage Vehicle washing on impermeable surfaces increases runoff on the streets, picking pollutants up off roads and transporting them to stormdrains. Wash water contains soaps, oils, greases, and emission fallout particles. Wash cars over permeable surfaces such as lawns or aerated soils Use soaps that do not contain phosphorus: this nutrient will promote overgrowth of algae in aquatic ecosystems. Avoid washing underneath the car over impermeable surface areas. This is the site of oil, grease, and fuel buildups 3.2 Disposal of Toxic Substances Never dump products labeled poisonous, corrosive, caustic, flammable, inflammable, volatile, explosive danger, warning, caution, or dangerous outdoors, into stormwater drains, sinks, toilets or drains. Oils, antifreeze, and used car batteries can be taken to the small boat harbor. Other hazardous materials are collected from Skagway on a designated day. 3.3 Lawn care and Landscaping 10 Pullen Creek runs through many parcels of private property. Proper lawn care can contribute to stormwater management by providing an area of infiltration for water running off sidewalks and roofs. Lawn care also has the potential to heighten pollution for stormwater runoff through the overuse of fertilizers and pesticides. Pesticides contain toxic chemicals, some of which are harmful to aquatic organisms at even low levels. Fertilizers and organic materials like grass clippings and leaves contain nutrients that promote algae overgrowth. According to the EPA, residential lawns produce significant amounts of runoff, and are therefore poor stormwater management tools, especially when they contain pesticides and fertilizers. This runoff can be contained in the lawn area with some structural practices. Avoid the use of pesticides, insecticides, fungicides, and rodenticides. If used, follow the directions carefully and do not over apply. Aerate compacted soils in areas of high runoff to promote water infiltration. Gardens have higher rates of infiltration because soils have larger pore spaces and root systems are more extensive compared to those of grass. Adding gardens to lawns also contribute to Skagway’s reputation as the Garden City of Alaska. Properly dispose of yard wastes: the area of Seven Pastures has a site for leaves, branches, and grass clippings. Riparian buffers are a structural BMP that provides a protective barrier to the creek. A riparian buffer is an area of native vegetation between a stream, creek or other waterbody and any type of development. These vegetative structures are the most important element of a stream ecosystem. Not only do they act as a filter for pollutants by allowing infiltration of water, they also create habitat for insects and wildlife. Stormwater that runs through buffer zones is slowed down by the increase in surface roughness (Liu et. al 2008). Contaminants are absorbed by the soil, which has high permeability due to root growth. Plants then take up nutrients and other pollutants before they can seep into groundwater or surface water. A 10 to 20 foot buffer of native grasses and trees can significantly decrease the amount of pollutants entering a stream or creek, adds to the aesthetics of the environment, and provides food and building materials for aquatic insects and animals (Zhang et al. 2009). Other structural BMPs that residents can employ on their own properties include rain barrels and rain gardens. Rain barrels collect water that runs off roofs and stores it for later use. This water can be used for washing or watering plants, decreasing the amount of city water used for these activities. Rain gardens are constructed basins that hold permeable soils as well as plants. These are best placed adjacent to areas of impermeable surface, where runoff can be directed into the gardens before contributing to the city’s stormwater volume. On properties that contain portions of Pullen Creek, maintain or establish a riparian buffer of 10 to 20 feet that is made up of native plants, trees, and grasses. 11 This reduces property maintenance area and also improves the condition of the stream on location as well as downstream Install a rain barrel in an area that collects roof runoff Create a rain garden in areas of high runoff that will add to property aesthetically while capturing stormwater and pollutants 3.4 Pet Wastes To prevent fecal coliform bacteria from entering the watershed and to help reduce the effects of nutrient overload, residents need only pick up after their pets Carry a bag on walks and adventures with your pet, dispose of waste in trash receptacles. Keep pet waste in residential yards under control and be especially mindful about areas around stormdrains and gutters. Section 4. Municipal 4.1 Roads In Skagway, a large source of sediments to the creek is sand and salt added to icy winter streets. In the spring, during melting days, the sediment is mobilized and the finest sediments are transported to stormdrains, affecting fish and insect habitat. Sweep up sand left after melts quickly and avoid washing debris into stormdrains. Installing oil water separators, sediment traps or inserts in stormdrains to capture pollutants. Regularly maintain them Snow removal is another potential stormwater issue. Accumulated snow can contain pollutants such as salt, sand, gravel, oil grease, antifreeze, heavy metals, and trace elements from engine emissions. A DEC report found that in study areas in Juneau and Anchorage, chromium, lead, and mercury were found at levels above established limits while litter and debris were most concerning to the public. The presence of pollutants suggest that dumping snow in marine environments, as some communities do because of lack of space, would create a water quality issue. In Skagway, municipal snow removal consists of pushing snow to the side of the road on all streets, with Broadway as the exception. From 1st to 7th along Broadway, snow is picked up and transported to the Southeast corner of the fenced in area by the small boat harbor. Whether this poses a stormwater problem is conditional on the proximity to Pullen Creek and the drainage area around the pile of snow. As it melts, collected pollutants could be carried into the creek 12 directly or via stormwater infrastructure. There is no dumping of snow into aquatic environments, fresh or marine, in Skagway, but the placement of snow could greatly affect Pullen Creek when it melts and carries pollutants. Evaluate the placement of snow removed from streets and where the runoff will go. Treatment BMPs such as sediment traps or infiltration basins (discussed in 4.2) may be installed to prevent pollutants from entering stormwater infrastructure. If possible, place removed snow in areas where melt will not affect streams or creeks. Dirt roads that abut the creek and are not maintained often have potholes that suggest finer sediments have traveled off the road. These holes fill with water and vehicles traveling through them cause water to wash over the banks carrying sediments. Create barriers between dirt roads and the creek with riparian buffers. Maintain these roads by filling in potholes to stop the process of road movement into the stream. 4.2 Outfalls Outfall site design can impact stream habitat negatively if the pipe diameter is too small, causing erosion at the discharge site. With proper construction, discharge sites can be engineered to dissipate energy and improve fish habitat. Build new outfall structures or modify existing ones to minimize impacts to aquatic organisms and their habitats by maintaining a maximum flow velocity of less than 10 feet per second. Pair each outfall with a rock splash pad, unless flow velocity is greater than 10 feet per second, in which case, more elaborate engineered structures should be explored such as a flow dispersal trench, a tightline system, or a gabion outfall. Tightline System A pipe that conveys flows down a steep slope with proper energy dissipation at the discharge site. Flow Dispersal Trench A trench dug specifically for receiving concentrated flows. Gabion Outfall Constructed area where water can pool up, reducing erosion that occurs due to flows. 13 Outfalls can also be paired with a widened stream at the discharge site, resulting in an alcove for fish to use as shelter during high flow velocities. 4.3 Vegetation On municipal lands that contain portions of Pullen Creek, riparian buffers can be established. Some areas along Pullen Creek are very steep and may benefit from stabilization measures using materials such as rocks or netting. Several riparian enhancement projects along Pullen Creek have been implemented over the years and have transformed unstable stream banks into vegetated areas with improved structural and habitat characteristics. TIWC, USFWS, SAGA1 and WP&YR have partnered in these projects to improve streamside areas to the benefit of the community, visitors, and stream ecosystem. Set aside a 10 to 20 foot strip of vegetation to protect streams from pollutants, erosion, and other sediments contributed by stormwater run-off. Stabilize banks with rocks, netting, or other materials to prevent erosion in steep areas. A biofiltration swale is another vegetated stormwater mitigation strategy. These are concave channels of vegetation that are either wet or dry and slow water that is flowing off impermeable surfaces or from stormdrain outfalls. The slowed water velocity allows for sediments and pollutants to fall out before the water is conveyed to rivers or streams. Dry swales are planted with grasses and are appropriate along streets, parking lots, and next to buildings. Wet swales are planted with wetland vegetation and are found in areas that tend to collect water or in constructed wetlands. Swales are constructed with permeable but not highly erosive soils such as sandy loam, loamy sand, or loam soils. The plants must withstand high velocity flows of water and be established in soils well before high velocity flows are expected. Suggested setbacks for swales are two feet from property lines, and 10 feet from building foundations. Create a depressed area with grasses and soil appropriate for characteristics of site flow and sediment quantities to intercept stormwater flows. Monitor and maintain them as needed. An infiltration basin, like a swale, is a depressed area that collects stormwater off an impermeable surface, often through a pipe or other conveyance element. In contrast to a swale, an infiltration basin will store the stormwater until it seeps through the soil and into groundwater. Some basins have pipes underneath that convey the water away from the area and some rely on the natural permeation characteristics of the site. This type of 1 A service program in the realm of AmeriCorps 14 mitigation strategy is appropriate for small drainage areas with low levels of sedimentation expected. Sediments will clog the system and result in failure. Construct an infiltration basin to convey surface runoff to groundwater while providing storage and pollution filtration. Plants will take up pollutants while water seeps through layers of soil. 4.3 Litter Litter is harmful to water quality and can disturb insect and fish habitat. It detracts from the natural beauty of the area and lets off toxins as it decomposes. Increase the number and visibility of garbage cans in high pedestrian areas around Pullen Creek. Develop signs that remind visitors and residents to be responsible with their garbage. Use several languages to effectively communicate with visitors from around the world. Section 5. Commercial 5.1 Vehicles Tourism is Skagway’s greatest source of revenue, and also its greatest source of pollution. On rainy days it is especially apparent how much pollution tourism vehicles add to the streets, which are streaked with fuel oil and contain puddles from leaks. Regularly perform checks and maintenance to prevent leaks and spills. Hold vehicle drivers responsible for these tasks and for the consequences of failing to perform them (i.e. cleaning up after spills). Make clean up materials available and easy to find. Create a spill clean-up plan and train vehicle drivers to follow it. Require responsible fueling. Many lines of fuel oil on roads may be from overfilling tanks. 5.2 Vehicle Washing Washing commercial vehicles on impermeable surfaces creates a large influx of stormwater and pollutants associated with vehicles in the stormwater system. Set aside a commercial vehicle-washing area containing the proper filtration systems to take out pollutants 15 Use soaps that are phosphorus free. 5.3 Construction In many communities, Stormwater Pollution Prevention Plans (SWPPP) are a required element of a construction process. SWPPP are site-specific documents outlining steps for reducing stormwater pollution caused by construction activities that clear land of vegetation. Some general guiding principles have been identified as effective BMPs to incorporate into these plans for reducing sediments to waterbodies. These are listed below. Minimize Clearing and Grading. Sites can be analyzed for areas where clearing and grading can be avoided. Aquatic areas are especially dependent on stream buffers, forest conservation areas, wetlands, springs, and seeps, highly erodible soils, steep slopes, and stormwater infiltration areas. Disturbing these areas should be avoided, if possible, or restricted to only necessary activities. Protect Waterways. When waterways are a part of a construction site, any land clearing along the riparian areas should be avoided. To protect the stream from excess sediment loading, a silt fence or earthen dike can be installed as a buffer. Stabilize Drainage Ways. A map of the existing future drainage patterns can inform the construction team about which way sediments will be heading. These drainage ways can be protected from erosion and sediment overload with netting, erosion control blankets, grass plantings, dikes, or silt fence. Implement Phase Construction. Grading areas only when needed rather than grading the entire site will reduce the time that soils are at risk of erosion. This may require more planning, but will result in stabilized soils throughout the construction process. Stabilize Loose Soils Quickly. Soil is stabilized by setting a goal of establishing a grass or mulch cover within two weeks of soil exposure. This practice can reduce sediment loads in local streams by a factor of six. If vegetation is not established, then mulch can serve as a stabilizing agent. Protect Steep Slopes. Erosion risk is highest along steep slopes. The best practice is to avoid clearing any slopes altogether and to divert runoff that would otherwise travel down the slope. If water cannot be diverted, then a silt fence to catch eroding sediments at the foot of the slope may prevent them from running into waterbodies. Slopes can be stabilized with erosion control blankets and mulch binders. 16 Establish Perimeter Controls. Perimeter controls such as silt fences or earth dikes help to keep sediments from the construction site within a contained area. These measures can stop the flow of runoff or even filter sediments out of runoff. Construct Advanced Settling Devices. Should storms occur and lead to fine sediment mobilization, stormwater drainage should lead to a basin where sediments can fall out. These basins are designed according to site conditions. Certify Contractors To Implement SWPPP. The most carefully thought out plan will not work if it is not implemented correctly. Therefore, the responsibility needs to be delegated to a contractor who is trained in installing and maintaining SWPPP measures that will lead to proper stormwater management. Adjust Plan for Field Conditions. Plans will be modified as needed according to the conditions of the construction site. Inspection of the construction site and the plan for mitigating impact should help revisions that will lead to appropriate modifications in instillation and implementation. Assess Stormwater Practices after Storms. Storms events can wash away or damage stormwater mitigation elements. Careful inspection of practices will allow contractors to repair and reinforce constructed elements to continue effective management of the Stormwater plan Section 6. Building, Repair, and Maintenance of Boats and Ships Skagway’s small boat harbor has many practices in place already that help reduce pollution to local waters. Some of these include: Fuel and oil spill clean up plans: The harbormaster attends annual SEAPRO (Southeast Alaska Petroleum Resource Organization) training to prepare for possible oil spill response. Clean up materials are readily available at the fueling station Materials for larger spills are accessible for harbor staff and other SEAPRO responders in the City of Skagway The voluntary, non-regulatory Clean Harbors Program was created by the Cook Inletkeeper, a non-profit community-based organization working to protect Alaska’s Cook Inlet. This program encourages harbors to reduce wastes and meet regulatory environmental requirements, which will reduce the risk of future fines. The process is voluntary and requires adherence to a list of best management practices. Certified Clean Harbors promote Alaskan fisheries, culture, and tourism by keeping hydrocarbons and other toxins out of watersheds. Even without Clean Harbor certification, harbors can implement steps that result in large improvements to marine environmental health. Boat 17 repair, maintenance, and fueling are all activities that can be carefully managed to prevent water quality deterioration. Major repairs and cleaning should be completed in the shipyard rather than in the water Refuse and waste materials from minor repairs and cleaning should be collected and disposed of onshore. Title XII of Skagway Municipal Code defines refuse of all kinds, including paint, oil, and dock sweepings, as nuisances and therefore unlawful (12.08.090 D). Topping off fuel tanks should be avoided as it leads to spills. Absorbent pads should be on hand in case spills do occur Engines and other mechanics should be maintained to prevent leaks into the bilge Bilge water should be carefully disposed of. Any oil should be soaked up with pads or pillows that are kept on board all vessels. Mixing soaps with oily bilge water is more toxic than oil alone.2 For more information on the Alaska Clean Harbors program, visit http://alaskacleanharbors.org/ or contact Rachel Lord at 907.235.4068 ext. 29. Section 7. Community Involvement Community involvement in watershed conservation fosters a connection to and appreciation for local rivers, lakes, and streams. This will continually promote healthy watersheds by creating a lasting social conscientiousness. In some communities, volunteer water monitoring programs have been constructed to connect residents with their water resources. These programs are all set up differently: they can be connected to local, state, interstate, or federal agencies and are funded through grants, endowments, fundraisers, and partnerships with organizations and businesses. Many of them work with local agencies that provide information, training, and technical assistance. Community involvement is one of the most effective means to promote stewardship of resources and allows a hands-on educational experience for the people who influence the health of the resource the most. Residential actions, large or small, add up to important changes in the quality of the resource, either for the better or for the worse. Community monitoring programs also foster connections between concerned citizens and agency staff that can be valuable for working for the present and future health of community resources. A related, and wider-sweeping effort is the adopt-a-stream program. These are often sponsored and supported by municipalities. The groups that have adopted the stream will engage in activities that improve the stream by collecting information on the stream and working on projects that reduce wastes in the present and the future. Some projects that have benefit some streams have included streambank enhancement, stream clean-ups, insect monitoring, and implementing water monitoring programs. 2 http://inletkeeper.org/clean-water/clean-boating/clean-boaters 18