South County Coastal Areas Beaches & Creeks

Background Information

On February 10, 2010, the San Diego Regional Water Quality Control Board (“San Diego Water Board”) adopted indicator bacteria Total Maximum Daily Loads (TMDLs) for impaired beaches and creeks in the San Diego Region. This includes TMDLs for over nine and a half miles of Orange County beaches, the entire length of Aliso Creek and the lower mile of San Juan Creek. A map of the affected areas is provided below.

South Orange County Indicator Bacteria Impaired Beaches and Creeks

Regulatory Description

The Beaches and Creeks TMDLs define the allowable indicator bacteria loads from the stormdrain system that will still allow attainment of water quality standards. The modeled reductions required to meet these loads in south Orange County range from 73-99% during dry weather to 91-100% during wet weather depending on the location and indicator bacteria species. A 22% wet weather allowable exceedance frequency of TMDL number target is also included in the TMDLs to account for natural sources of bacteria. Compliance with the TMDLs must occur by April 4, 2021 with a possible extension to April 4, 2031 for wet weather load reductions.

Indicator bacteria can come from a variety of sources throughout the watershed including pet waste, trash, sewage spills, septic tanks, animal manure fertilizers, and natural sources such as bird and wildlife feces and decaying plant material. During wet weather, storm runoff picks up the bacteria and associated pathogens off of the land and deposits them into recreation waters through the municipal separate storm sewer system (MS4). During dry weather groundwater seepage and nuisance flows from urban land use activities such as car washing, sidewalk washing, and lawn over-irrigation provide transport through the MS4.

San Juan Creek Mouth at Doheny Beach. Birds are believed to be a major source of indicator bacteria to Doheny State Beach.

Impaired Beaches

The impaired beaches and creeks addressed in the Beaches and Creeks TMDLs are based upon the 2002 Clean Water Act Section 303(d) list developed using water quality data collected prior to 2002. Since 2002 water quality at many south Orange County beaches has significantly improved. This is due in part to Best Management Practices (BMPs) implemented by the County, cities, non-governmental organizations, and the public in an effort to reduce bacteria and associated pathogens. These efforts have included but not limited to diversion structures, stormdrain inlet filters, treatment facilities (Dana Point Salt Creek Ozone Treatment Plant), wetlands (Wood Canyon Emergent Wetland Project), irrigation controllers, beach cleanups, the use of pet waste bags, and public outreach and education efforts.

Alipaz drain within the City of Dana Point, before and after diversion. Photos courtesy of the City of Dana Point.

Achieving the bacteria TMDL targets will not be easy and it is anticipated that future reductions plans will require a multitude of similar efforts. As a first step, watershed Bacteria Load Reduction Plans (BLRPs) or Comprehensive Load Reduction Plans (CLRPs) targeting all watershed pollutants of impairment are being developed outlining the BMPs needed to meet TMDL targets and special studies to identify sources of indicator bacteria in the watershed. Under the current MS4 permit, Water Quality Improvement Plans (WQIPs) are being developed that, by incorporating key elements of both BLRPs and CLRPs, will achieve receiving water quality targets, including those specified in the bacterial TMDLs. For South Orange County, one single WQIP will be developed that covers all watersheds.

Concurrently with the WQIP effort, the San Diego Region Beaches and Creeks TMDLs are under significant revision by a joint effort of Regional Board, City and County of San Diego, and County of Orange. To ensure that the revised TMDL is scientifically sound, reasonably achievable, and protective of public health, a series of studies including reference study, epidemiological study, quatitative microbial risk assessment, cost-benefit analysis, among others, have been commissioned. The results of these studies will support the revision of the TMDL, which is anticipated to be adopted in 2018.