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July 15, 2005 The Water Report <br />Urban <br />Stormwater <br />Recreational <br />Use? <br />"Tributary <br />Rule" <br />Application <br />V. <br />Reality <br />Culvert <br />Standard <br />Economic <br />Analysis <br />In another example, many of Los Angeles' storm drains are enumerated expressly in the region's <br />water quality control plan, including a vertical - walled, concrete -lined box culvert that runs three miles <br />from downtown Los Angeles to Culver City (shown in the accompanying photo, previous page). Such <br />listed storm drains historically have been regulated as if they were suitable for body- contact recreational <br />uses, defined as follows: <br />"Uses of water for recreational activities involving body contact with water, where ingestion of water is <br />reasonably possible. These uses include, but are not limited to, swimming, wading, water - skiing, skin <br />and scuba diving, surfing, white water activities, fishing, or use of natural hot springs." <br />The Los Angeles regional water quality control board (the "regional board ") rejected its own staff's <br />recommendation to modify the recreational use designation for the drain shown in the photo. Last year, <br />however, the California State Water Resources Control Board (SWRCB) restored some common sense to <br />policy by amending this designation.. <br />In other cases, the regional boards have extrapolated water quality standards upstream into storm <br />drains pursuant to the so- called "Tributary Rule" (the Tributary Rule is contained in many of California's <br />regional water quality control plans).(8) Under the Tributary Rule, these agencies improperly assume <br />that storm drains and other upstream drainages automatically have the same water quality standards as the <br />downstream waters into which they drain. For example, the Tributary Rule in the Los Angeles water <br />quality control plan states: <br />"Those waters not specifically listed (generally smaller tributaries) are designated with the same <br />beneficial uses as the streams, lakes, or reservoirs to which they are tributary. This is commonly <br />referred to as the `tributary rule. "' <br />The Tributary Rule is being used to regulate municipalities as if they are discharging to waters that <br />constitute a source of public water supplies, or a place in which to swim, or a habitat for fisheries. The <br />reality — known to the agencies — is demonstrably to the contrary. <br />For example, on the basis of the Tributary Rule, Vacaville, a small city in the Central Valley of <br />California, is being held to treatment standards for its wastewater plant based on protection of public <br />water supplies and cold water fisheries. The reality is that the discharge is to a hydrologically modified <br />creek dominated by treated wastewater and agricultural tailwater. Although regional board "staff <br />considered the uses and concluded that they did not exist and were highly unlikely to exist in the <br />future, "(9) on the basis of the Tributary Rule the agency applied these beneficial uses because of open <br />waters many miles downstream of the plant's discharges.(10) <br />Similarly, in 2001, drinking water and swimming standards for Newport Bay in Orange County were <br />extrapolated upstream to a vertical - walled, fenced -off concrete box culvert draining downtown Santa <br />Ana. Since the standards were not met within the box culvert, the regional board recommended the <br />culvert be slated for a Total Maximum Daily Load ( "TMDL" — a CWA- derived pollutant load <br />allowance). Fortunately, in February 2003, SWRCB rejected the regional board's TMDL <br />recommendation. However, these examples reflect the tendency of the MS4 permit writers to improperly <br />assert jurisdiction and standards to inland storm drainage structures. <br />Unintended Consequences <br />Review of the administrative record for the Los Angeles region water quality control plan reveals a <br />major problem with applying the water quality standards to urban runoff. In short, the primary economic <br />analysis by the agency to assess compliance costs was performed in the early 1970s — well before it was <br />contemplated that urban runoff would be subject to the standards. In fact, urban runoff was purposely left <br />out of the 1970s' economic analysis on the basis that it was an "uncontrollable nonpoint source," and was <br />"impractical to attempt to treat. "(11) At that time, the California agencies considered urban runoff to be <br />"nonpoint" in nature and thus not subject to the NPDES permitting required for point sources. <br />THE LOS ANGELES REGIONAL BOARD STATED IN PERTINENT PART: <br />"With respect to uncontrollable nonpoint sources, such as urban ... runoff, there may be certain things <br />that the public can accomplish to lessen the impact, even though much of the effect is unavoidable. No <br />specific nonpoint source control facilities are proposed ... It is impractical to attempt to treat runoff <br />generally... No specific financial provisions are considered for the control of nonpoint sources of <br />pollution." <br />After Congress in 1987 directed that urban runoff be subject to NPDES permitting and control, the <br />regional board did not undertake a meaningful economic analysis of what it would take to render urban <br />runoff compliant with water quality standards. In general, regional boards typically assert that the BMPs <br />specified in MS4 permits will somehow bring about compliance with water quality standards. However, <br />there never has been a study identifying BMPs actually capable of rendering all urban runoff, or even a <br />substantial portion thereof, consistently compliant with the standards. <br />Copyright© 2005 Envirotech Publications; Reproduction without permission strictly prohibited. 3 <br />