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 />
|