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Accomplishments
Fecal
Total Maximum Daily Loads for Santa Monica Bay Beaches
In January 2002, the Los Angeles Regional Water Quality
Control Board (RWQCB) adopted a dry-weather Fecal Bacteria
Total Maximum Daily Load (TMDL) for Santa Monica Bay
beaches. A TMDL is the maximum amount of a pollutant,
in this case fecal bacteria, that a water body can receive
and still meet water quality standards set to protect
the beneficial uses of that water body. The Santa Monica
Bay fecal bacteria TMDL for dry weather will prohibit
any beach from exceeding the state health standards
during the summer months (April through October). All
beaches must be cleaned up and in compliance by 2006.
For dry weather conditions outside of the summer month
time period (November through March), no beach in Santa
Monica Bay will be allowed to exceed bacterial standards
more than 3 times of the daily dry weather days sampled.
In
December 2001, the Regional Water Board unanimously
approved the wet weather fecal bacteria TMDL. The new
regulations will protect the health of swimmers and
surfers by greatly reducing fecal bacteria at beaches
in wet weather. The regulation covers 44 beaches from
Palos Verdes to Ventura County line. Santa Monica Bay
watershed cities and the County will have 10 years to
reduce the number of days that exceed state health standards
to a number less than or equal to water quality conditions
seen at pristine beaches in undeveloped watersheds,
such as Leo Carillo Beach in Malibu. This averages out
to about 17 days for Venice, Santa Monica, Pacific Palisades
and Malibu Beaches. As a point of comparison, Malibu
Surfrider Beach currently exceeds water quality standards
more than fifty days per year. Under no circumstances
will beaches be allowed to have water quality worse
than exists today, which is critical for those beaches
that only exceed water quality standards about five
times a year or less.
The
State Water Resources Control Board subsequently unanimously
approved both bacteria TMDLs. These were the first major
beach TMDLs in the state to be adopted. This process
was a result of a 1998 consent decree entered into between
Heal the Bay, the Santa Monica Baykeeper, NRDC, and
the EPA.
EPA's
draft Implementation Guidance for Ambient Water Quality
Criteria for Bacteria, 2002 version.
The United States Environmental Protection Agency or
USEPA was expected to issue the final draft Implementation
Guidance for Ambient Water Quality Criteria for Bacteria,
2002 version in April 2003. This document is meant to
provide guidance to States for the adoption and implementation
of federal bacteria standards into their beach management
programs. California already did this when it adopted
AB-411. Heal the Bay has worked hard over the past two-years
(with the U.S. EPA's staff in Washington D.C.) to develop
a document that will help states develop conservative
and effective public health programs at recreational
beaches. However, the only piece of good news in the
document is that EPA requires States to use both the
geometric mean and single sample bacteria standards
at beaches.
As
mentioned in earlier sections, there are a significant
number of shortcomings with the guidance document, each
of which further reduces the health protection of recreational
water users. The first major issue with the document
is the fact that the EPA is allowing States to nearly
double the acceptable risk level at freshwater beaches,
from 8 illnesses per 1000 swimmers to 14. Also, EPA
supports the use of a variable standard for bacterial
indicators depending on beach usage. In other words,
EPA says that it is acceptable for a beachgoer to swim
in more contaminated water at Leo Carrillo Beach in
Malibu than at Venice City Beach, simply because Leo
Carrillo Beach is frequented by fewer people. The proposal
calls for allowing enterococcus densities to be three
times higher at less frequented beaches, which means
swimmers and surfers will have a much greater chance
of getting sick. Finally, EPA did not provide any justification
for "allowable risk rates" - the number of acceptable
illnesses among recreational water users.
EPA's
National Beach Guidance and Grant Performance Criteria
for Recreational Waters
Last year, the USEPA published the National Beach Guidance
and Grant Performance Criteria for Recreational Waters
(otherwise known as the nationwide beach water quality
monitoring and public notification program). As currently
written, however, there are considerable shortcomings
in the program as proposed. For example, USEPA will
allow for monthly sampling frequencies at some beaches,
no required timeframe in which to notify the public
of water quality exceedances, no consistent sampling
techniques, and no required and consistent method by
which to notify the public when beach water quality
has been exceeded. USEPA's original goal (to develop
a national standardized monitoring and reporting program
for beaches) will simply not be achieved with the program
as it's proposed. The program neither adequately guides
health officers to establish meaningful monitoring programs,
nor does it provide beachgoers with adequate health
protection. Finally, USEPA has failed to incorporate
key components from California's statewide beach bathing
water monitoring and public notification program into
this program. USEPA should have developed a rigorous,
model beach program that would protect public health,
and through which states that would implement all or
most of the program would be eligible for increased
Federal BEACH funding amounts. USEPA refused to do this
because many eastern states want continued funding of
their inadequate monitoring programs.
Criteria
for Listing a Beach on the State's List of Polluted
Waters 303(d) list
The Clean Water Act requires states to identify beaches
that are too polluted to be safe for swimming and then
to clean these beaches up to applicable health standards.
Heal
the Bay has made a number of recommendations to the
State Water Resources Control Board (SWRCB) on the methodology
used to identify impaired beaches for this list (also
called a 303(d) list):
-
Listing should be based primarily on the number of
exceedances of the State microbiological health standards
(both the single sample and geometric mean standards)
as demonstrated by historical routine monitoring data
and other sources of water quality data such as special
studies.
- A
minimum of 3 to 5 years of data should be analyzed
when making a listing decision.
- Listing
decisions should not be influenced by information
that is not directly related to water quality at the
beach such as whether enforcement action is occurring
or can be taken, the source of the contamination,
or whether a TMDL is an "appropriate" means
of mitigating the problem.
- The
number of exceedances that result in the listing of
a beach should be determined by comparing the beach
to a reference beach. Arbitrarily allowing a 10% or
even 4% rate is not supported by existing monitoring
data. An analysis of historical daily monitoring data
from Santa Monica Bay beaches shows many beaches have
exceedance rates below 4%, indicating that very low
exceedances rates can be achieved even though natural
sources of fecal bacteria exist.
-
Beaches that are permanently posted with warning signs
should automatically be listed.
- Rain
advisories should be used in the listing process for
beaches that are not monitored at least weekly during
wet weather or during the non-AB411 season.
In
addition to these recommendations, at beaches impacted
by flowing storm drains or freshwater outlets, Heal
the Bay urged the SWRCB and the local health agencies
to relocate routine monitoring stations so that they
would be directly in front of the stormdrain, which
would help identify impaired beaches and polluted outlets.
Currently, routine monitoring occurs anywhere from directly
in front of the drain to 83 yards from the drain, depending
on the monitoring agency. Thus, by using monitoring
data from stations located away from the drain, the
state is allowing a de facto mixing zone around the
storm drain. In the mixing zone, water quality can exceed
standards but the beach is not identified as impaired.
In other words, the state is taking away the beneficial
use (swimming) along these sections of beach. The state
is allowing this to occur although swimmers and surfers
can often be found directly in front of flowing storm
drains and creeks.
Malibu
Creek Fecal Bacteria TMDL
Malibu Creek and Lagoon are polluted with fecal bacteria
at levels that often greatly exceed the State health
standards for swimming. The pollution could be coming
from many sources, including urban runoff, horse related
activities, and malfunctioning septic systems. A TMDL,
or pollution limit, would solve this serious problem
if it is developed and implemented effectively. Unfortunately
the Bacteria TMDL recently proposed by the EPA for Malibu
Creek is seriously flawed, and Heal the Bay believes
it will not solve the fecal bacteria problem in the
Malibu Creek watershed or achieve the goal of a clean
and safe Surfrider Beach. The proposed TMDL is based
predominately on fecal coliform densities even though
epidemiological studies conducted by the EPA itself
showed E. coli, not fecal coliform, is associated with
health risks from swimming in polluted freshwater. The
TMDL also fails to address enterococcus loads into Malibu
Lagoon and from the Lagoon to Surfrider Beach: generally
the most polluted beach along Santa Monica Bay. Finally,
the TMDL uses a completely inappropriate reference site
(the saltwater Leo Carillo beach) to determine how many
days the Malibu Creek watershed will be allowed to exceed
health standards due to the impacts of bacteria from
natural sources, such as birds and wildlife. Based on
this reference site, the EPA is proposing to allow three
days of exceedances of health standards during the dry
season, even though the TMDL did not demonstrate any
need to allow exceedances due to natural sources. In
addition, the TMDL potentially violates the Clean Water
Act's antidegradation provision and fails to include
a required margin of safety. Heal the Bay believes the
proposed TMDL, once in place, will not restore the beneficial
use (swimming) throughout Malibu Creek watershed and,
importantly, at Surfrider Beach. The Los Angeles Regional
Water Quality Control Board is planning to revise the
TMDL by the end of this summer.
Rapid
Methodologies for Detecting Bacteria Indicators and
other Potential Indicators of Fecal Contamination
Through the California Beach Initiative, the State
of California is funding research on the rapid detection
of microbiological indicators of fecal contamination.
Rapid detection technology has the potential to greatly
improve protection of public health at recreational
waters and our ability to track and identify sources
of fecal contamination. Several methodologies
look promising, however, there are many technical
hurdles that must be tackled before we see these technologies
used routinely in beach monitoring such as high detection
limits, specificity issues, and viability
measurement problems. Measuring specific
strains of bacteria is not compatible with the currently
available epidemiological data and measuring specific
viruses has limited use because we currently do not
know the etiology of many illnesses associated with
swimming in fecal contaminated waters. In addition,
detection limits of the methods, often related to the
required prefiltration and concentration of the sample,
are much greater than levels of fecal contamination
that may cause illness. Heal the Bay believes it will
be several years before a rapid methodology for beach
monitoring is ready for routine use on the beach.
One
methodology that increases the speed of the chromogenic
substrate method currently used by many public health
agencies may be available sooner and could speed up
detection from 18 to 24 hours to around 6 hours.
San
Diego's Mission Bay Health Effects Study
Beginning this Memorial Day, the Southern California
Coastal Waters Research Project, UC Berkeley, and the
County and City of San Diego will initiate the first
ever epidemiological study at an enclosed beach on the
Pacific Coast. The study will include a number of beach
locations in Mission Bay and conclude this summer. Researchers
will attempt to determine if there are health risks
associated with swimming at polluted beaches in Mission
Bay. Also, researchers will attempt to find the actual
pathogenic viruses that can make swimmers sick. The
results should be out before our next annual Beach Report
Card.
Recommendations
Advocate
for Year-Round Postings along the Entire Length of Beach
Impacted by Flowing Storm Drains
In southern California, there is little consistency
among counties monitoring storm drain impacted beaches
regarding where to collect a sample, when to post
a warning sign, and where to post the warning sign.
For
example,
samples are collected from the
wave wash
(where
the creek, river, or storm drain meet the ocean water)
to as far as 83 yards from the drain, depending on
the county. Also, state regulations require posting
a warning sign when samples exceed the
single sample standard,
but give local health departments discretion to post
a warning sign if the 30-day geometric-mean standard
is exceeded. The counties of Santa Barbara,
Ventura,
and Los Angeles and the City of Long Beach
post a warning signs if there is a single sample exceedance;
the County of Orange will post warning signs for both
a single
sample standard or 30-day geometric mean exceedance;
and the County of San Diego will initially only post
warning
signs on a single sample exceedance but will continue
that
posting if subsequent sampling causes an exceedance
of either the single sample or 30-day geometric mean
standard. Lastly, the location of the warning sign
depends
on where the samples are collected and therefore is
highly variable.
To
address these three points, Heal the Bay recommends
permanently posting warning signs along the entire
length of beach adjacent to flowing storm drains
where water
quality may fail to meet the State health standards
for both the single sample and 30-day geometric
mean standards.
This is based on the results of the Storm Drain Plume
Dispersion study Heal the Bay completed with the
Southern
California Coastal Water Research Project (SCCWRP),
and represents a change from the current posting
protocol
implemented by health agencies.
The
Storm Drain Plume Dispersion study looked at how
fecal
bacteria discharged from storm drains disperses along
the shoreline and the impacts on the plume by ocean
and discharge conditions. The study shows that the
length
of beach made unsafe for swimming is beach-specific
depending on local beach topography, and can vary
over
the course of a few hours. The study also shows that
beach health standards can be exceeded at distances
much greater than that covered by monitoring stations
routinely sampled be local health agencies (well
over
100 yards in some cases). Based on these results, Heal
the Bay believes the protocol typically used by County
health agencies for posting warning signs may not
be
adequately notifying swimmers of potential health risks
around freshwater outlets in Southern California.
We
recommend the following improvements to the current
system:
-
The beach adjacent to a polluted storm drain or freshwater
outlet should be posted with warning signs over the
entire length of beach where water quality is affected
by the plume of fecal bacteria discharging from the
drain. .
- Since
the length of beach where water quality may be impacted
by high fecal bacteria levels is beach-specific, we
recommend this length be determined by completing
multiple sampling events at multiple locations around
the drain under varying oceanographic conditions.
- Once
the length of beach impacted has been determined,
the routine monitoring location should be moved to
the wave wash (the location where the creek, river,
or storm drain effluent meets the ocean). The beach
should remain permanently posted until routine monitoring
at the drain shows fecal bacteria densities are below
all health standards.
Advocate
for increased funding for California's shoreline monitoring
program from EPA's BEACH program
Currently, the State receives $535,000 to implement
a statewide shoreline water quality monitoring and
public
notification program at popular beaches. State allotments
are based on three criteria: the length of the beach
season, the amount of beach miles, and estimated beachgoers.
Although California receives the largest grant available
for this program, the allotment criteria used by EPA
has a major shortcoming that has prevented California
from receiving additional funds to cover the cost of
monitoring. The problem with the allotment methodology
is the lack of criteria for determining the strength
of a state's monitoring program or public notification
protocol. EPA does not provide an incentive or disincentive
to move states beyond even the most basic
water
quality monitoring and public notification program.
For example, states may monitor for only one fecal
bacteria
indicator, or may not notify the public about water
quality exceedances in a timely manner, yet those
states
receive full funding while other states,
such as California, monitor for three fecal bacteria
criteria, and notifies the public immediately of any
water quality exceedances. Heal the Bay believes EPA
should consider the quality of the monitoring program
when allocating funding to the States.
Advocate
for Improved Public Notification of Poor Water Quality
at Open-ocean Beaches
Most of the beaches in Southern California are
located on the open ocean, receive excellent natural
flushing by the incoming swell, and and are not located
near a
source of human sewage. At these
"open-ocean" beaches Heal the Bay believes health agencies
should use the discretion afforded to them in State
regulation (AB-411) to consider factors such as historical
water quality, the magnitude of the exceedance, and
the number of indicators that exceed the standards
when deciding if a warning sign should be posted.
Currently, most
counties rigorously post warning signs when the single
sample standards are exceeded. Recent research, however,
indicates high variability in fecal bacteria densities
can occur at open-ocean beaches. This high variability
combined with the lag time of 18 to 48 hours from sample
collection time to posting time can result in erroneous
public notification of water quality. Thus, at open-ocean
beaches where there are no potential sources of human
sewage, Heal the Bay supports the State regulation
that allows health officials to consider multiple
factors
before posting a warning sign. In contrast, exceedances
of the geometric mean standards at open-ocean beaches
can indicate a chronic water quality problem. However,
currently, most health agencies do not post the beach
with a warning sign when the geometric mean standards
are exceeded. Heal the Bay urges health agencies to
post open-ocean beaches with warning signs when the
geometric mean standard is exceeded and to conduct
a
sanitary survey to find the source of the contamination.
Advocate
for the Los Angeles County, Department of Health Services
to resume weekly water quality monitoring at Mothers'
Beach in Marina del Rey
Since September 2000, the County has not done
any shoreline monitoring at Mothers' Beach, relying
solely on the City of Los Angeles' single sample location.
As has been demonstrated in past years in our Beach
Report Card, water quality at Mothers' Beach and other
enclosed beaches can vary significantly within a short
distance. Mothers' Beach is the only enclosed beach
in all of southern California with only one sampling
station. Other enclosed beaches, such as Kiddie Beach
in Ventura County, Baby Beach in Orange County, and
Avalon Beach on Catalina Island, which are much smaller
in beach area, have multiple monitoring stations to
better characterize overall water quality. By reducing
the total number of samples collected and beach area
covered, County Health Services has, in effect, deprived
the public of their right to know about accurate water
quality conditions, and thus impacted their ability
to make an informed decision about attending this beach.
Unfortunately this situation will not improve until
the approval of the Total Maximum Daily Load for fecal
bacteria in Marina del Rey, which will require additional
sampling locations at Mothers' Beach.
Ensure
best management practices are implemented and
promote implementation of tidal
circulation improvements at enclosed beaches
Beaches such as Kiddie Beach in Channel Island
Harbor, Mothers' Beach in Marina del Rey, Cabrillo Beach
in Los Angeles Harbor, Baby Beach in Dana Point Harbor
and a number of beaches in Mission Bay all received
fair to poor water quality marks, and all are popular
with children and young families. Whether the pollution
problem is due to a lack of tidal circulation or the
beach's proximity to a pollution source, young beachgoers
are far too frequently exposed to poor water quality
conditions. One of Heal the Bay's highest priorities
is to ensure that these chronically polluted beaches
are cleaned up.
Encourage
agencies to monitor water quality at popular beaches
year-round (beyond the AB411 required
dates of April-October)
Year-round monitoring provides winter beachgoers
(usually surfers who frequent the beach due to winter
swells) with important information about water quality.
In California there is no set beach season. Surfers,
swimmers, divers, wind-surfers, and kayakers use the
water year-round, so all of these ocean enthusiasts
have the right to know about water quality at their
favorite beaches on a year-round basis.
Assist
Northern California Coastal Counties in developing
their monitoring programs and databases
Heal the Bay will continue to work, where needed,
with the Environmental Health Departments in Del Norte,
Humboldt, Mendocino, Marin, San Francisco, and San Mateo
to ensure that the necessary resources exist for them
to develop adequate monitoring and public notification
programs and database systems.
Advocate for the State to enforce Sanitary Survey
Protocols as established in AB 538 and The Ocean Plan
In an effort to do more than just notify beachgoers
of potential water quality problems at their favorite
beaches, AB 538 was passed to require sanitary surveys
(source investigations) to be completed at those beaches
where water quality problems exist. The intent was to
determine where beaches with water quality problems
existed, identify the causes of impairment, and implement
the necessary strategies to abate the pollution source.
The requirement of a source investigation is not a new
concept - it was stipulated by the Ocean Plan in 1988.
However, the state never enforces or requires municipalities
to conduct these surveys when exceedances occur. The
Ocean Plan states that ".if a shore station consistently
exceeds a coliform objective or exceeds a geometric
mean.the Regional Board shall require the appropriate
agency to conduct a survey to determine if that agency's
discharge is the source of the contamination." (State
Water Resources Control Board Ocean Plan 1997) AB 538
states that source investigations shall be conducted
"if bacteriological standards are exceeded in any three
weeks of a four-week period, or for areas where testing
is done more than once a week, 75 percent of testing
days that produce an exceedence of those standards.
Advocate for full funding of the Beach Water Quality
Source Identification and Technical Assistance Projects
Two years ago, Governor Davis, as part of the
Clean Beach Initiative, allocated $1.5 million for research
on rapid pathogen indicators and pathogen source identification
efforts. The results of their research effort should
be available before next year's Beach Report Card. Unfortunately,
this funding was only a fraction of the amount needed
to adequately study beach pollution issues. Given the
importance of coastal tourism to the California economy
- the Natural Resources Defense Council estimated that
$37 billion was generated by coastal tourism in their
1999 "Testing the Waters: A Guide to Water Quality at
Vacation Beaches" - Heal the Bay strongly recommends
that $20 million be allocated to conduct necessary scientific
studies, including pathogen detection and quantification
methods, a source identification methodology, a characterization
of runoff sources and reduction in nuisance flows, and
health-effect studies for wet-weather exposures, and
multiple exposures. On a positive note, the Southern
California Coastal Water Research Project will soon
release a study on the effectiveness of a variety of
state-of-the-art microbiological source identification
techniques methods used for identifying and quantifying
fecal pollution sources. Although funding research in
this economy presents major challenges, understanding
beach pollution problems, their cause, the fate and
transport of pathogens and pathogen indicators, and
the human and marine impacts of exposure to polluted
runoff and pathogens, will help us to better protect
our coastal resources. This recommendation has been
echoed by the State Water Resources Control Board's
Beach Water Quality Workgroup.
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