SR 09-13-2016 9A
Ci ty Council
Report
City Council Meeting : September 13, 2016
Agenda Item: 9.A
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To: Mayor and City Council
From: Susan Cline, Director , Public Works, Water Resources
Subject: Hold a Public Hearing on Report on Water Quality and Public Health Goals
Recommended Action
Staff recommends that the City Council h old a public hearing ; rece ive public comments
on the City of Santa Monica Report on Water Quality Relative to Public Health Goals ;
and accept the report.
Executive Summary
Provisions of the California Health and Safety Cod e section 116470 require public water
systems serving more than 10,000 customers to prepare a report every three years that
includes information on the detection of any elements the water at levels above Public
Health Goals (PHG ’s) or the equivalent Maximum Contaminant Level Goals (MCLG ’s).
PHGs are adopted by th e State Office of Environmental Health Hazard Assessment and
MCLGs are set by the United States Environmental Protection Agency (EPA). A public
hearing is required to accept and receive public comments on the report.
Staff has prepared the attached repor t (Attachment A) to provide information on the
quality of its drinking water supply relative to adopted Public Health Goals and
Maximum Contaminant Level Goals.
Background
The re is strong public interest and concern about the safety of drinking water nat ionally
and here in California. Sophisticated testing can now trace infinitesimal traces of
potentially hazardous elements in water sources. The California legislature has
established the concept of a Public Health Goal (PHG). PHGs are established by the
California Environmental Protection Agency (Cal/EPA) Office of Environmental Health
Hazard Assessment (OEHHA). A PHG is a health risk assessment, not a proposed
drinking water standard. It is the level of a contaminant in drinking water, which is
conside red not to pose a significant risk to health if consumed for a lifetime. This
determination is made without regard to cost or treatability. The State Water Resource
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Control Board (SWRCB)/Division of Drinking Water (DDW), formerly the California
Departmen t of Public Health, uses PHGs in the evaluation of health -related drinking
water standards, known as Maximum Contaminant Levels (MCLs). The Division of
Drinking Water uses Public Health Goals to identify Maximum Contaminant Levels that
are to be reviewed for possible revision or when setting new Maximum Contaminant
Levels for unregulated chemicals.
California State Water Code section 116470 require s that large water utilities (more
than 10,000 service connections) prepare a special report every three years if their
water quality measurements have exceeded any PHGs in the three previous calendar
years. The current report covers years 2013, 2014, and 2015. The law also requires
that where OEHHA has not adopted a PHG for a contaminant, the water suppliers ar e
to use the Maximum Contaminant Level Goal (MCLG) adopted by the United States
Environmental Protection Agency (USEPA). MCLGs are the federal equivalent to
PHGs, but are not identical. Only contaminants w hich have a California primary
drinking water sta ndard and for which either a PHG or MCLG has been set are to be
addressed in this report.
Discussion
In June 2016 , the City of Santa Monica sent out its Annual Water Quality Report, which
is available online at http://www.smgov.net/departments/publicworks/water.aspx . Along
with information regarding important current water issues, the annual report includes
information required by the Federal and State Governments to illustrate how t he quality
of the water at the consumer’s tap compares against established water quality
standards. These water quality standards are established by Federal and state
regulations as Maximum Contaminant Levels (MCL ’s) and Notification Levels (NL ’s).
MCLs are the highest level of a contaminant allowed in drinking water, and NLs are the
concentrations of a contaminant which, if exceeded, trigger treatment or other
requirements that public water systems must follow. Consistently, Santa Monica’s water
is show n to be in full compliance (below all regulated MCLs and NLs) with all Federal
and State regulatory water quality standards. Furthermore, recent reports prepared by
the City of Santa Monica address the City’s ongoing efforts to maintain a safe and
reliable water supply, including the 2015 Urban Water Management Plan
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(http://www.smgov.net/uploadedFiles/Departments/Public_Works/Water/2015_UWMP_
Final_June_2016.pdf ), and the February 201 6 information item addressing Santa
Monica’s control of lead in drinking water
(http://www.smgov.net/uploadedFiles/Departments/Public_Works/Water/Lead_in_Drinki
ng_Water_20160222.pdf ).
The attached report (Attachment A) has been prepared pursuant to the requirements of
the State Health and Safety Code. For the period from 2013 to 2015 in Santa Monica,
Public H ealth G oals were exceeded for seven unique elements : Lead, Copper, Arsenic,
Uranium, Radionuclides, Bromate, and Chromium VI . Further details about each of
these element’s characteristics, health risks, and treatment technologies are presented
in the full Public Health Goals Report . Although these elements exceed Public Health
Goals, Santa Monica’s drinking water meets all State and Federal drinking water
standards. S ubstances in the City’s water supply are below the applicable MCLs
required by these regulatory agencies and no additional actions are recommended for
the treatment of the City’s potable water supply a t this time . As both treatment
technology and health risk assessments evolve, standards for these elements may be
altered in the future, but Santa Monica continues to meet or exceed the state of the art
levels of water purity.
Copies of the report are a vailable for public review at the City Clerk’s office, Water
Resources Division office s , the Main Library, and online at
http://www.smgov.net/departments/publicworks/water.aspx . A public notice advising of
the availability of the report was published in t he Santa Monica Daily Press on August
30, 2016 and September 6, 2016 .
Environmental Analysis
The City of Santa Monica Report on Water Quality Relative to Public Health Goals is
categorically exempt from the California Water Quality Act (CEQA) as a Class 8
exemption (Section 15308 of the CEQA Guidelines), actions by regulatory agencies for
the protection of the environment.
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Financial Impacts & Budget Actions
There is no immediate financial impact or budget action necessary as a result of the
recommended a ctions. Meeting all the new Public Health Goals for all elements is
beyond the current limits of financial feasibility for Santa Monica water customers.
Prepared By: Gil Borboa, Water Resources Manager
Approved
Forwarded to Council
Attachments:
A. PHG Report 2016 Draft 6 -30 -16 with Exhibits A -F
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CITY OF SANTA MONICA
REPORT ON WATER QUALITY
RELATIVE TO PUBLIC HEALTH GOALS
June 2016
BACKGROUND
The California legislature has established the concept of a Public Health Goal (PHG).
PHGs are established by the California Environmental Protection Agency (Cal/EPA)
Office of Environmental Health Hazard Assessment (OEHHA). A PHG is a health risk
assessment, not a proposed drinking water standard. It is the level of a contaminant in
drinking water, which is considered not to po se a significant risk to health if consumed
for a lifetime. This determination is made without regard to cost or treatability. The
State Water Resource Control Board (SW RCB)/Division of Drinking Water (DDW),
formerly the California Department of Public Health, uses PHGs in the evaluation of
health-related drinking water standards, known as Maximum Contaminant Levels
(MCLs). DDW uses PHGs to identify MCLs t hat are to be reviewed for possible revision
or when setting new MCLs for unregulated chemicals.
Provisions of the California Health and Sa fety Code Section 116470(b) (Exhibit A)
require that large water utilities (>10,000 se rvice connections) prepare a special report
by July 1, 2016 if their water quality meas urements have exceeded any PHGs in the
three previous calendar y ears. The law also require s that where OEHHA has not
adopted a PHG for a contaminant, the wate r suppliers are to use the Maximum
Contaminant Level Goal (MCLG) adopted by the United States Environmental
Protection Agency (USEPA). MC LGs are the federal equivalent to PHGs, but are not
identical. Only constituents which have a California primary drinking water standard
and for which either a PHG or MCLG has been se t are to be addressed in this report.
Exhibit B is a list of all regulated cons tituents with MCLs and PHGs or MCLGs.
There are a few constituents that are rout inely detected in water systems at levels
usually well below the drinking water standar ds for which no PHG nor MCLG have yet
been adopted by OEHHA or USEPA. These include total trihalomethanes (TTHMs)
among others.
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This report provides the following informati on as specified in the Health and Safety
Code (Exhibit A) for each consti tuent detected in the City of Santa Monica’s (City) water
supply in 2013, 2014, and 2015 at a level e xceeding an applicable PHG or MCLG:
• Numerical public health risk associated with the MCL and the PHG or MCLG
(Exhibit C).
• Category or type of risk to health t hat could be associated with each
constituent.
• Best Available Treatment Technolog y that could be used to reduce the
constituent level.
• Estimate of the cost to install that treatment if it is appropriate and feasible.
WHAT ARE PHGs?
• PHGs are set by the Califo rnia Office of Environmental Health Hazard Assessment
(OEHHA) which is part of Cal/EPA.
• PHGs are based solely on public health risk considerations. None of the risk-
management factors that are considered by DDW in setting drinking water standards
are considered in setting the PHGs. T hese factors include analytical detection
capabilities, treatment technology available, benef its and costs.
• PHGs are not enforceable and are not requ ired to be met by any public water system.
MCLGs are federal equivalent to PHGs and are set by the USEPA.
WATER QUALITY DATA CONSIDERED
All of the water quality data collected for Santa Monica’s water system between 2013
and 2015 for purposes of determining compli ance with drinking water standards were
considered. This information was summariz ed in tables included in the Annual Water
Quality Reports made available to all Santa Monica customers, residents, and
businesses in June 2014, June 2015 and June 2016 (Exhibit D).
Most of the constituents tested in the wate r were reported as Not Detected (ND) and are
not generally listed in the Annua l Water Quality Reports. W hen a constituent is reported
as ND, it generally means that the laboratory did not detect the compound, but it could
also mean that it was detect ed at a level less than California’s Detection Level for
purposes of Reporting (DLR).
GUIDELINES FOLLOWED
The Association of California Water A gencies (ACWA) formed a workgroup, which
prepared guidelines for water utilities to us e in preparing the PHG reports. These
guidelines were used in the preparation of this report. No general guidelines are
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available from the state regulatory agencies. ACWA’s workgroup also prepared
guidelines for water utilities to use in estima ting the costs to reduce a constituent to the
MCL. Exhibit E provides cost estimates for the best treatment technologies that are
available today.
BEST AVAILABLE TREATMENT TECHNOLOGY AND COST ESTIMATES
Both the USEPA and DDW have adopted what are known as Best Available
Technologies (BATs), which are the best known methods of reducing contaminant
levels. Capital construction and operati on and maintenance (O&M) costs can be
estimated for such technologies. Howe ver, since many PHGs and MCLGs are set
much lower than the MCL, it is not always possible or feasible to determine what
treatment is needed to further reduce a constit uent down to or near the PHG or MCLG.
For example, USEPA sets the MCLG for potential cancer-c ausing chemicals at zero.
Estimating the costs to reduce a constituent to zero is difficult, if not impossible,
because it is not possible to verify by analyt ical means that the level has been lowered
to zero. In some ca ses, installing treatment to try and further reduce very low levels of
one constituent may have adverse effect s on other aspects of water quality.
CONSTITUENTS DETECTED THAT EXCEED A PHG OR A MCLG
The following is a discussion of constituents t hat were detected in one or more of the
City’s drinking water sources at levels ex ceeding the PHG, or if no PHG exists, above
the MCLG. For some constituents su ch as Total Coliform Bacteria and
Trichloroethylene, no detections above the MCLG or PHG occurred during the period
covered by this report, but have appeared in previous PHG reports and are discussed
again for comparison purposes. Santa Monica consistently delivers safe water at the
lowest possible cost to its customers usi ng multiple treatment methods approved by
DDW. Constituents that were detected in one or more drinking water sources at levels
above the MCLs are reduced to acceptable le vels. The health risk information for
regulated constituents with MCLs, PHGs or MCLGs is provided in Exhibit C.
Total Coliform Bacteria
Total coliform bacteria are measured at approx imately 100 sites around the City. No
more than 5% of all samples collected in a month can be positive for total coliforms.
This defines the MCL. Alt hough there is no PHG for total co liform bacteria, the MCLG is
zero positive samples. The reason for the total coliform drinking water standard is to
minimize the possibility of the water cont aining pathogens, which are organisms that
cause waterborne disease. Because total co liform analysis is only a surrogate indicator
of the potential presence of pathogens, it is not possible to state a specific numerical
health risk. While USEPA normally sets MCLGs “at a level where no known or
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anticipated adverse effects on per sons would occur”, EPA indicates that it cannot do so
with total coliforms. Nevertheless, without th e ability to determine a specific numerical
risk, the MCLG has been set at ze ro for total coliform bacteria.
Coliform bacteria are a group of indicator or ganisms that are ubiquitous in nature and
are not generally considered harmful. They are used because of the ease in monitoring
and analysis. If a positive sample is found, it indicates a potential problem that needs to
be investigated with follow-up sampling. It is not at all unusual for a system to have an
occasional positive sample. In Santa Moni ca, about 80 of the sites where samples are
taken for total coliform bacteri a are taps, typically hose bibbs, on private residences or
businesses. Many of these taps are exposed to the environment and while they provide
a satisfactory sample point most of the ti me, occasionally the tap itself may become
exposed to bacteria from the environment, e.g. overgrown plants, pets and humans.
When samples are drawn from these exposed taps , they test positive on rare occasion.
During the period covered by this repor t, the City collected between 119 and 142
samples each month for total coliform analysi s. No samples were found to be positive
for total coliform bacteria fo r calendar years 2013 - 2015.
In an effort to reduce the potential for posit ive results due to taps exposed to the open
environment, the Water Resources Division (Div ision) has a program to prioritize the
sites and install more dedicated sampling stations. The dedicated samplers are
enclosed in a lockable box an d are protected from the en vironment. Two new boxes
were installed during the period covered by th is report with plans to complete more in
the future in conjunction with the Divis ion’s main line replacement program.
The Division already maintains an effe ctive cross connection control program, a
disinfectant residual throughout the system, an effective monitoring and surveillance
program, and positive pressure in all parts of the distribution system. The Division has
already taken all of the steps described by the DDW as Best Available Technology
(BAT) for Coliform Bacteria in Section 6447, Ti tle 22, CCR. Since it is unlikely that any
change to the treatment proce ss at the Arcadia Water Treat ment Plant would prevent
the occasional positive test result at the distribution sampling site s, staff recommends
no change to the existing treatment.
Trichloroethylene (TCE)
The PHG for trichloroethylene (TCE) is 0.0017 milligrams per liter (mg /l). The MCL for
TCE is 0.005 mg/l. The level of TCE in the City’s groundwat er and supplemental
supplies was below the MCL and PHG at all ti mes during the period of this report.
Trichloroethylene is a volatile organic compo und (VOC). It is a manmade solvent used
since the 40's and 50's as a degreaser, parts cleaner , and in other industries. In the last
several decades, TCE has shown up increasingl y in groundwater s upplies in Southern
California and elsewhere. TCE was discover ed at low levels in several of the City’s
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wells located along or near Olympic Boulevar d in 1980. Initially the TCE from the
Olympic Wells was diluted in the mixture wit h other, uncontaminated wells. As the TCE
levels increased over time, several wells had to be turned off until treatment to remove
the TCE could be installed. In 1992, the Division completed an expansion and upgrade
to the Arcadia Treatment Plant that included mechanical aerat ion to remove TCE in the
combined well flow to a level below the MC L of 0.005 mg/l. The contaminated Olympic
Wells were placed back in service and we re blended and treated in this way until
December 2010 when the City’s new Revers e Osmosis (RO) softening plant was
commissioned. The new plant includes a decarbonator unit that now provides
additional removal of TCE.
The level of TCE in the water produced by the Arcadia Treatment Plant ranged from ND
to 0.0007 mg/l for the period covered in th is report. The annual average TCE produced
at the treatment plant was 0.0005 mg/l in 2015 and ND for 2013 and 2014.
The category of health risk associated with TCE, and the reason that a drinking water
standard was adopted for it, is that people w ho drink water containing TCE above the
MCL for many years could experience an increased risk of getting cancer. DDW says
that “Drinking water which meets this st andard (the MCL) is associated with little to
none of this risk and should be considered safe with respect to TCE.” This language is
taken from the California Code of Regulati ons (CCR), Title 22, Section 64468.2. The
numerical health risk of ingesting drin king water with TCE above the PHG is 1X10 -6 , or
one additional theoretical cancer case in one million people drinking two liters of water a
day for 70 years. The health risk of i ngesting water with TCE above the MCL is six
additional theoretical cancer cases in one million people.
The Best Available Technology (BAT) for TC E to lower the concentration below the
MCL is either adsorption using liquid phase Granular Activat ed Carbon (GAC) or
Packed Tower Aeration (PTA). However, bec ause the new RO softening plant includes
a decarbonator system that is very similar to PTA, the level of TCE is now consistently
and reliably below the PHG for TCE. Theref ore, no recommendation for further action is
advised.
Lead and Copper
There are no MCLs for lead or copper. Lead and copper are not present in our water
sources, but can leach into drinking wate r through the resident’s plumbing systems and
faucets. Instead of MCLs, ev ery three years a set of special samples is collected and
the results evaluated to determine whether the City’s water system has achieved
“optimized corrosion control”. The samples collect ed are first-draw at t he tap of thirty or
more homes identified as high-risk (new plum bing installed with lead solder before it
was banned). To meet drinking water st andards, the 90th percentile reading (meaning
90% of the samples were lower) of all sa mples collected by the City from these
household taps cannot exceed an Action Level (AL) of 0.015 mg/l for lead and 1.3 mg/l
for copper. The PHG for lead is 0.0002 mg/l and the PHG for copper is 0.3 mg/l.
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The last round of testing for lead and copper was conducted by the Water Resources
Division in 2013 (next round is summer 2016). The 90 th percentile reading for lead in
the last round was 0.0028 mg/l and was 0.13 mg /l for copper. These are below the
Action Levels, which means t he City continued to meet wate r quality standards for lead
and copper and was again considered to have “optimized corrosion control”. The value
for copper was lower than the PHG, but t he level for lead was higher than its
corresponding PHG.
There are two categories of health risk associated with lead - chronic toxicity
(neurobehavioral effects in child ren, hypertension in adults) and cancer. The numerical
health risk of ingesting drinking water with lead above the PHG is 2X10 -6 , or two
additional theoretical cancer cases in one million people drinking tw o liters of water a
day for 70 years.
As stated previously, the City’s water supply is considered to have “optimized corrosion
control”. In general, optimizing corrosion c ontrol is considered to be BAT to address
corrosion issues and any lead and copper fi ndings. The Division will continue to
monitor water quality parameter s that relate to corrosivi ty such as pH, hardness,
alkalinity and total dissolved solids and will ta ke action, if necessary to maintain our
system in an “optimized corrosion control” condition.
Since the City’s water supply continues to meet the “optimized corrosion control”
requirements, it is not prudent to initiate additional corrosion contro l treatment until such
time as changing conditions might warrant further action. Therefore, no estimate of cost
has been included in this report and no recomm endations for further action are advised.
Arsenic
The PHG for arsenic is 0.000004 mg/l. The MC L for arsenic is 0.01 mg/l. Arsenic is a
naturally occurring metallic element found in water generally at low levels throughout
California and elsewhere due to the erosion of mineral deposits. It can also enter water
supplies from runoff from agricultural and indu strial sites. The MCL was lowered in
2006 due to increasing evidence of potential detrimental heal th effects even at low
levels. The concern is that long-term exposur e to arsenic in drinking water may cause
skin damage or problems with circulat ory systems, and may cause cancer.
Arsenic was below the MCL in all of the Cit y’s water sources at all times during the
period covered in this report, however se veral sources exceeded the PHG during 2014
and 2015. Arsenic readings for all sources for the period covered by this report ranged
from ND (Reporting Limit was 0.002 mg/l) to a high of 0.0033 mg/l in the water
purchased from the Metropolit an Water District’s (MWD) Jensen Treatment Plant. The
annual average for the Jensen s upply ranged from ND to 0.0033 mg/l for the period
covered by this report and ND to 0.0021 mg/l for the Weymouth supply.
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Local groundwater supplies had annual averages for this period that ranged from ND
(Reporting Limit was 0.0005 mg/l) to 0.001 mg/l for Santa Monica Well #1. No detection
of arsenic was found in water coming from the Arcadia Treatment Plant and the annual
average for arsenic in water produced by the treatment plant was ND for calendar years
2013 - 2015.
The category of health risk associated wit h arsenic is that people who drink water
containing arsenic above the MCL for m any years could exper ience an increased
cancer risk. The numerical health risk of i ngesting drinking water with arsenic above the
PHG is 1X10 -6 , or one additional theoretical cancer cases in one million people drinking
two liters of water a day for 70 years.
There are two BATs designated for arsenic removal, Ion Exchange and Reverse
Osmosis (RO). As previously stated, t he City’s RO softening plant was commissioned
in December 2010 and as expected, is achievi ng reduction of arsenic to below the level
it can be measured. Please note that BAT s are designed for treatment to achieve
compliance with the corresponding MCL only, and not PHGs. It is unlikely that arsenic
will be removed to a level lower than the very low PHG for arsenic. In any case, that
level is lower than laboratory tests can det ect, so it would be impossible to confirm
whether water coming from t he Arcadia Treatment Plant, or any given water supply,
actually has arsenic lower than the PHG le vel because it cannot be measured at that
level.
It is not practical or feasible to estimate costs for the reduction of arsenic from the
supplemental water the City purchases from MWD or Santa Monica Well #1, so no such
determination will be attempted here and no recommendations for further action are
advised.
Uranium
The PHG for uranium is 0.43 picoCuries per liter (pCi/l) and the MCL is 20 pCi/l.
Uranium is a naturally occurring metallic el ement which is weakly radioactive and is
ubiquitous in the earth’s crust. Uranium is found in ground and surface waters due to its
natural occurrence in geological formations . The average uranium concentrations in
surface and ground water are 1 and 2 pCi/l respec tively. The uranium intake from water
is about equal to the total fr om other dietary components.
Uranium was below the MCL for all water sour ces at all times during the period covered
in this report, however all sources exceeded the PHG at least once during this period.
Uranium readings for the period covered by this report ranged from 1.5 pCi/l to a high of
2.7 pCi/l in the water coming from the Arc adia Treatment Plant. Annual averages for
the water coming from the plant ranged from 1.7 to 1.9 pCi/l for calendar years 2013 -
2015. Annual averages for the water coming from MWD’s Weymouth and Jensen
supplies ranged from ND (Reporting Limit was 1 p Ci/l) to 3 pCi/l for the period covered
by this report.
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The category for health risk associated with uranium is that people who drink water
containing uranium above t he MCL for many years coul d experience an increased
cancer risk. OEHHA has determined that th e numerical cancer risk for uranium above
the PHG level is 1x10 -6 , or one additional theoretical cancer cases in one million people
drinking two liters of water a day for 70 years.
There are several BATs designated to lower uranium to below the MCL including RO.
As previously stated, the City’s RO softening plant was commissioned in December
2010 and as expected, is achieving some reduction of uranium from the City’s
groundwater supply. However, BATs are designed for treatm ent to achieve compliance
with the corresponding MCL only, and not PHGs, so this addition of a BAT for uranium
did not achieve reduction of uranium to bel ow the PHG. Further treatment to reduce
uranium at the Arcadia Tr eatment Plant is neither practical, nor feasible.
The City’s single well not treat ed by the Arcadia Treatment Plant is Santa Monica Well
#1. The water for this well had a uranium leve l that ranged from ND (Reporting Limit is
0.7 pCi/l) to 0.8 pCi/l for the period cover ed by this report and so must be evaluated for
treatment for removal of uranium to bel ow the PHG. Of the designated BATs for
uranium, the most effective and economical approach would be to us e RO treatment at
the well site. Based on 2015 flow rates and esti mated costs, this would be in the range
of $332,000 per year not including the cost for waste (bri ne) disposal. However, this
well is located in the center median of S an Vicente Blvd in a residential neighborhood
where it would not be feasible to construct ev en a small treatment plant at the well site.
Again, it is also unclear whether treatment to below t he PHG for uranium could be
achieved using RO, as BATs are designed to achieve compliance only to the
corresponding MCL. It should also be noted that this cost estimate may be imprecise
as treatment costs can vary widely dependin g on the particulars of the situation.
It is not practical or feasible to estimate costs for the reduction of uranium from the
supplemental water the City purchases from MWD, so no such determination will be
attempted here and no recommendations for further action are advised.
Other Radionuclides
There are several radionuclides for which OEHHA has not set PHGs, but for which an
MCLG has been designated by USEPA. The st andards are for radionuclides including:
alpha emitters, beta/photon emitters, comb ined radium as well as the standard for
uranium described above. In addition to these standards, USEPA has designated an
MCLG of zero for each. The groundwater and supplemental water supplies for Santa
Monica are below the MCLs for these consti tuents at all times during the period covered
by this report, but the MCLGs of zero for some of these radi onuclides were exceeded at
some sources at various times during this period.
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Radionuclides are radioactive elements that are found in nature or are man-made.
They are unstable and emit particles or wave s of high energy from the nucleus or other
parts of the atom. Th ere are three basic kinds of high-ener gy radiation: alpha, beta, and
gamma (included in a broader group called photons ). Many radionuclides emit more
than one kind of radiation, but are classified by their most important kind. The MCL for
alpha emitters limits the level of “gross alpha” radiation other than what is contributed by
uranium and radon. The MCL fo r beta/photon emitters limits t he level of radiation from
a group of 179 man-made radioactive materials. The MCL for combined radium limits
the radiation on two kinds (or “isotopes”) of radium: radium-226 and radium-228. These
MCLs were adopted to address concern with the health effects from radiation inside the
body after consuming the radionuclides as evidence suggests that long-term exposure
to radionuclides in drinking water may cause cancer.
The level of alpha emitters in the City’s groundwater and supplemental supplies was
below the MCL of 15 pCi/l at all times durin g the period covered by this report, but
exceeded the MCLG of zero in some moni toring data. Gross alpha readings for the
period covered by this report ranged from ND (Reporting Limit was 2 pCi/l) for all
supplies at various times to a high of 5 pCi/l in the water coming from MWD’s Jensen
Plant in 2014. Annual averages ranged from ND for some of the suppl ies to 3 pCi/l for
water coming from Jensen.
The standard for beta/photon emitters does not apply to the City’s groundwater and as
such, is not covered by this report. Howeve r, the supplemental wa ter the City receives
from MWD met the MCL of 50 pCi/l for beta/photon emitters at all times, but exceeded
the MCLG of zero in some monitoring data. Readings for beta/photon emitters for both
MWD supplies for the period covered by th is report ranged from ND (Reporting Limit
was 4 pCi/l) to a high of 6 pCi/l in the water coming from MWD’s Weymouth Treatment
Plant reported for 2014. The annual averages ranged from ND to 5 pCi/l for the Jensen
and Weymouth supplies respectively, for the period covered by this report.
The level of combined radium in the Cit y’s groundwater and supplemental supplies was
below the MCL of 5 pCi/l at all times duri ng the period covered by this report. No
detections of combined radium were reporte d for the City’s supp lies or MWD imported
water from Weymouth and Jensen plant.
The BATs for these radionuclides are the same as for uranium. As previously stated,
the City’s RO softening plant was commissi oned in December 2010 and as expected, is
achieving some reduction of these other radionuclides from the City’s groundwater
supply. As explained previously, BAT s are designed for treatment to achieve
compliance with the corresponding MCL only, and not PHGs, so this addition of RO
softening considered a BAT for these other r adionuclides did not achieve reduction to
below the MCLGs in all cases. Further tr eatment to reduce othe r radionuclides at the
Arcadia Treatment Plant is neither practica l, nor feasible. Likewise, the analysis for
treatment of Santa Monica Well #1 and the MWD supplies is the same as for uranium
and no recommendations for further action are advised.
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Bromate
The PHG for bromate is 0.0001 mg/l. The MCL for bromate is 0.010 mg /l. Bromate is a
disinfection byproduct (DBP) fo rmed when water containing naturally occurring bromide
ion is ozonated. The MCL for bromate does not apply to single readings but is instead
compared to a Running Annual Average (RAA).
The MCL was adopted in 2002 to address conc ern with potential health effects as
evidence suggests that long-term exposure to bromate in drinking water may cause
cancer. The standard applies only to wate r treatment plants t hat apply ozone for
disinfection or other purposes, and so does not apply to the City’s groundwater.
However, the supplemental water the City receives from MWD’s Jensen Treatment
Plant is ozonated and met the RAA MCL for br omate of 0.010 mg/l at all times, but
exceeded the PHG for the period covered by this report.
The Jensen Treatment Plant was retrofitt ed with ozone in 2005 as part of MWD’s plan
to implement ozonation at all six of their treatment plants. T he purpose of the retrofit is
to insure compliance with new requirements for disinfection of surface waters and new
DBP regulations, as well as an improvement in the plants’ ability to handle taste and
odor episodes resulting from periodic algal blooms in MWD’s source reservoirs. As
expected, the switch to ozone at the Jensen Treatment Plant result ed in reductions of
total trihalomethanes and haloacetic acids, wh ich are classes of DBPs that are also
regulated. However, bromat e itself is a DBP and the formation of which is a
consequence of the switch in disinfectant. Bromate readings for the Jensen Treatment
Plant for the period covered by this r eport ranged from ND (Repor ting Level is 0.001
mg/l) to 0.013 mg/l. The highest RAA was 0.008 mg/l for 2015 and demonstrated
compliance with the MCL as did all other RAAs for 2013 and 2014.
The category for health risk associated wit h bromate is that people who drink water
containing bromate above the MCL for many years could experience an increased risk
of getting cancer. OEHHA has determined that the numerical cancer risk for bromate
above the PHG level is 1x10 -6 , or one additional theoretical cancer cases in one million
people drinking two liters of water a day for 70 years.
The BAT to reduce bromate is control of the ozone treatment process to reduce
production of this DBP. As such, this is a process that is under the control and
jurisdiction of MWD, is already being conduc ted and will not be addressed further in this
report.
Hexavalent Chromium (Chromium VI)
A PHG for chromium VI was set at 0.00002 mg/L in July 2011. The MCL for chromium
VI was set at 0.01 mg/l in July 2014. The total chromium MCL of 0.05mg/l was
established in 1977 to address the non-cancer toxic effect of chromium VI.
Water Resources Division
June 2016 Page 11
Chromium is an odorless and tasteless metallic element. It is found naturally in rocks,
plants and can also be produced by industrial processes. The most common types of
chromium found in natural waters in the env ironment are chromium III and chromium VI.
Total chromium is the sum of chromium III and chromium VI. Chromium III and
chromium VI are covered t ogether under the total chromi um MCL because these forms
of chromium can convert back and fo rth in water depending on environmental
conditions.
Chromium III is an essential human dietary element and naturally occurs in many
vegetables, fruits, grains and yeast. Chromi um VI also occurs naturally in the
environment from the erosion of natural chromium deposits from rocks and can also be
released in the environment fr om industrial processes via storage leaks, discharges and
improper disposal practices.
Total chromium and chromium VI were below the MCL in all of the City’s groundwater
sources at all times, but ex ceeded the PHG for chromium VI at least once during the
period covered in this report. Suppl emental water from the Jensen and Weymouth
Treatment Plants had no detection of chromium or chro mium VI during this reporting
period.
Water coming from the Arcadia Water Treatm ent Plant had chromium VI levels that
ranged from ND (Reporting Limit is 0.00002 mg /l) to 0.0002 mg/l for the Arcadia
Treatment Plant.
The City’s single well not treat ed by the Arcadia Treatment Plant is Santa Monica Well
#1, which had levels for this peri od ranging from 0.0015 to 0.0016mg/l.
Chromium VI is known to be a potent carc inogen when inhaled. It was found to also
cause cancer in laboratory mice and ra ts when exposed through drinking water.
OEHHA has determined that the numerical cancer risk for chromium VI above the PHG
level is 1x10 -6 , or one additional theoretical cancer cases in one million people drinking
two liters of water a day for 70 years.
The recommended technologies for Chromium VI removal are weak base anion
exchange resin or reduction-co agulation-filtration technology. Weak base anion
exchange is considered the more cost-effectiv e of these two technologies. However,
neither is capable of reducing chromium VI to below 0.001 mg/l. The City’s new RO
softening plant is already achieving a great er reduction of chromium VI than these
alternate technologies.
It is unlikely that any tec hnology will be developed that c an reduce chromium VI to
below the very low PHG. In any case, that level is lower than laboratory tests can
detect, so it would be impossible to confi rm whether water coming from the Arcadia
Treatment Plant, or any given water supply, actually has chromium VI lower than the
PHG level because it cannot be measured at t hat level. Further treatment for the
Water Resources Division
June 2016 Page 12
removal of chromium VI is neither practical, nor feasib le, so no recommendations for
further action are advised.
RECOMMENDATIONS FOR FURTHER ACTION
The drinking water quality of the City of Santa Monica meets all SWRCB/Division of
Drinking Water and USEPA drinking water st andards set to protect public health. The
City’s RO softening plant commissioned in December 2010 is achieving further
reduction of many of the constituents identifi ed in this report from the City’s groundwater
supply. To further reduce the le vels of these constituents t hat are already significantly
below the established health-based Maxi mum Contaminant Levels (MCL) would
typically require that additional costly treatment processes be constructed. The
effectiveness of the treatment processes to provide any significant reductions in
constituent levels at these already low va lues is uncertain. The health protection
benefits of these further hy pothetical reductions are not clear and may not be
quantifiable. Therefore, no acti on is proposed at this time.
ADDITIONAL INFORMATION
1,4-Dioxane
No MCL, MCLG, or PHG exists for 1,4-Diox ane, and as such, is not a requirement for
this report. However, DDW has a Notifica tion Level (NL) for 1,4-Dioxane, which was
lowered to 0.001 mg/l in 2010. As reported to City Council in 20 02, the City’s Olympic
Wells (Santa Monica Wells 3&4) were found to have 1,4-Dioxane above the NL. The
City was advised by DDW in 2002 that it wa s acceptable to continue the use of these
wells as long as the level remained less than 100 times the NL. However, plans for the
construction of a new treatment plant tar geting 1,4-Dioxane and ot her contaminants in
the Olympic Wells are underway with an ant icipated completion date by 2020.
EXHIBITS:
A California Health and Sa fety Code Section 116470(b)
B List of Regulated Constituent s with MCLs, PHGs or MCLGs
C Numerical Health Risk Information
D Tables excerpted from Annual Wa ter Quality Reports for 2013 - 2015
E Cost Estimates for Treatment Technologies
F Acronyms
EXHIBIT A
Health & Safety Code
Section 116470 (b)
On or before July 1, 1998, and every thr ee years thereafter, public water systems
serving more than 10,000 service c onnections that detect one or more
contaminants in drinking water that exceed the applicable public health goal,
shall prepare a brief written report in plain language that does all of the following:
(1) Identifies each contami nant detected in drinking water that exceeds the
applicable public health goal.
(2) Discloses the numerical public heal th risk, determined by the office,
associated with the maximum contaminant level for each contaminant identified
in paragraph (1) and the numerical public health risk determined by the office
associated with the public healt h goal for that contaminant.
(3) Identifies the category of risk to pub lic health, including, but not limited to,
carcinogenic, mutagenic, te ratogenic, and acute toxicity, associated with
exposure to the
contaminant in drinking water, and incl udes a brief plainly worded description of
these terms.
(4) Describes the best available tec hnology, if any is then available on a
commercial basis, to remove the contamin ant or reduce the concentration of the
contaminant. The public water system may, solely at its own discretion, briefly
describe actions that have been taken on its own, or by other ent ities, to prevent
the introduction of the contaminant into drinking water supplies.
(5) Estimates the aggregate cost and the cost per customer of utilizing the
technology described in paragraph (4), if any , to reduce the concentration of that
contaminant in drinking water to a le vel at or below the public health goal.
(6) Briefly describes what action, if any, the local water purveyor intends to take
to reduce the concentration of the contam inant in public drinking water supplies
and the basis for that decision.
(c) Public water systems required to prepar e a report pursuant to subdivision (b)
shall hold a public hearing for the purpose of accepting and responding to public
comment on the report. Public water syst ems may hold the public hearing as part
of any regularly scheduled meeting.
(d) The department shall not require a public water system to ta ke any action to
reduce or eliminate any exceed ance of a public health goal.
(e) Enforcement of this section does not require the department to amend a
public water system's operating permit.
(f) Pending adoption of a public health goal by the Office of Environmental Health
Hazard Assessment pursuant to subdivisi on (c) of Section 116365, and in lieu
thereof, public water systems shall use the national maximum contaminant level
goal adopted by the United States Envi ronmental Protecti on Agency for the
corresponding contaminant for purposes of complying with the notice and
hearing requirements of this section. (g ) This section is intended to provide an
alternative form for the federally requi red consumer confidence report as
authorized by 42 U.S.C. Section 300g-3(c).
1 of 4
This table includes:
● DD W's maximum contaminant levels (MCLs)
● DD W's detection limits for purposes of reporting (DLRs)
Constituent MCL DLR PHG or (MCLG)Date of PHG
Aluminum 1 0.05 0.6 2001
Antimony 0.006 0.006 0.02 1997
Antimony ----0.0007 2009 draft
Arsenic 0.010 0.002 0.000004 2004
Asbestos (MFL = million fibers per liter; for fibers
>10 microns long)7 MFL 0.2 MFL 7 MFL 2003
Barium 1 0.1 2 2003
Beryllium 0.004 0.001 0.001 2003
Cadmium 0.005 0.001 0.00004 2006
Chromium, Total - OEHHA withdrew the 1999
0.0025 mg/L PHG in Nov 2001 0.05 0.01 (0.100)
Chromium, Hexavalent (Chromium-6) 0.01 0.001 0.00002 2011
Cyanide 0.15 0.1 0.15 1997
Fluoride 2 0.1 1 1997
Mercury (inorganic) 0.002 0.001 0.0012 1999 (rev2005)*
Nickel 0.1 0.01 0.012 2001
Nitrate (as N) 10 as N 0.4 45 as NO3
(=10 as N)1997
Nitrite (as N) 1 as N 0.4 1 as N 1997
Nitrate + Nitrite (as N)10 as N 0.4 10 as N 1997
Perchlorate 0.006 0.004 0.001 2015
Selenium 0.05 0.005 0.03 2010
Thallium 0.002 0.001 0.0001 1999 (rev2004)
Copper 1.3 0.05 0.3 2008
Lead 0.015 0.005 0.0002 2009
● PHGs for NDMA and 1,2,3-Trichloropropane (both are unregulated) are at the bottom of this table
● The federal MCLG for chemicals without a PHG, microbial contaminants, and the DLR for 1,2,3-TCP
Chemicals with MCLs in 22 CCR §64431 —Inorganic Chemicals
Copper and Lead, 22 CCR §64672.3
Values referred to as MCLs for lead and copper are not actually MCLs; instead, they are called "Action Levels" under the lead
and copper rule
2016 PHG Triennial Report: Calendar Years 2013-2014-2015
MCLs, DLRs, and PHGs for Regulated Drinking Water Contaminants
(Units are in milligrams per liter (mg/L), unless otherwise noted.)
Last Update: December 29, 2015
(Reference last update 9/23/2015: http://www.waterboards.ca.gov/drinking_water/certlic/drinkingwater/MCLsandPHGs.shtml)
● Public health goals (PHGs) from the Office of Environmental Health Hazard Assessment (OEHHA)
Exhibit B
2 of 4
Constituent MCL DLR PHG or (MCLG)Date of PHG
Gross alpha particle activity - OEHHA concluded
in 2003 that a PHG was not practical 15 3 (zero)n/a
Gross beta particle activity - OEHHA concluded
in 2003 that a PHG was not practical 4 mrem/yr 4 (zero)n/a
Radium-226 --1 0.05 2006
Radium-228 --1 0.019 2006
Radium-226 + Radium-228 5 --(zero)--
Strontium-90 8 2 0.35 2006
Tritium 20,000 1,000 400 2006
Uranium 20 1 0.43 2001
Benzene 0.001 0.0005 0.00015 2001
Carbon tetrachloride 0.0005 0.0005 0.0001 2000
1,2-Dichlorobenzene 0.6 0.0005 0.6 1997 (rev2009)
1,4-Dichlorobenzene (p-DCB) 0.005 0.0005 0.006 1997
1,1-Dichloroethane (1,1-DCA)0.005 0.0005 0.003 2003
1,2-Dichloroethane (1,2-DCA)0.0005 0.0005 0.0004 1999 (rev2005)
1,1-Dichloroethylene (1,1-DCE)0.006 0.0005 0.01 1999
cis-1,2-Dichloroethylene 0.006 0.0005 0.1 2006
trans-1,2-Dichloroethylene 0.01 0.0005 0.06 2006
Dichloromethane (Methylene chloride)0.005 0.0005 0.004 2000
1,2-Dichloropropane 0.005 0.0005 0.0005 1999
1,3-Dichloropropene 0.0005 0.0005 0.0002 1999 (rev2006)
Ethylbenzene 0.3 0.0005 0.3 1997
Methyl tertiary butyl ether (MTBE) 0.013 0.003 0.013 1999
Monochlorobenzene 0.07 0.0005 0.07 2014
Styrene 0.1 0.0005 0.0005 2010
1,1,2,2-Tetrachloroethane 0.001 0.0005 0.0001 2003
Tetrachloroethylene (PCE) 0.005 0.0005 0.00006 2001
Toluene 0.15 0.0005 0.15 1999
1,2,4-Trichlorobenzene 0.005 0.0005 0.005 1999
1,1,1-Trichloroethane (1,1,1-TCA)0.2 0.0005 1 2006
1,1,2-Trichloroethane (1,1,2-TCA)0.005 0.0005 0.0003 2006
Trichloroethylene (TCE) 0.005 0.0005 0.0017 2009
Trichlorofluoromethane (Freon 11)0.15 0.005 1.3 2014
1,1,2-Trichloro-1,2,2-Trifluoroethane (Freon 113)1.2 0.01 4 1997 (rev2011)
Vinyl chloride 0.0005 0.0005 0.00005 2000
Xylenes 1.75 0.0005 1.8 1997
[units are picocuries per liter (pCi/L), unless otherwise stated; n/a = not applicable]
Chemicals with MCLs in 22 CCR §64444 —Organic Chemicals
(a) Volatile Organic Chemicals (VOCs)
Radionuclides with MCLs in 22 CCR §64441 and §64443 —Radioactivity
Exhibit B
3 of 4
Constituent MCL DLR PHG or (MCLG)Date of PHG
Alachlor 0.002 0.001 0.004 1997
Atrazine 0.001 0.0005 0.00015 1999
Bentazon 0.018 0.002 0.2 1999 (rev2009)
Benzo(a)pyrene 0.0002 0.0001 0.000007 2010
Carbofuran 0.018 0.005 0.0017 2000
Carbofuran ----0.0007 2015 draft
Chlordane 0.0001 0.0001 0.00003 1997 (rev2006)
Dalapon 0.2 0.01 0.79 1997 (rev2009)
1,2-Dibromo-3-chloropropane (DBCP)0.0002 0.00001 0.0000017 1999
2,4-Dichlorophenoxyacetic acid (2,4-D)0.07 0.01 0.02 2009
Di(2-ethylhexyl)adipate 0.4 0.005 0.2 2003
Di(2-ethylhexyl)phthalate (DEHP) 0.004 0.003 0.012 1997
Dinoseb 0.007 0.002 0.014 1997 (rev2010)
Diquat 0.02 0.004 0.015 2000
Diquat ----0.006 2015 draft
Endrin 0.002 0.0001 0.0018 1999 (rev2008)
Endrin ----0.0003 2015 draft
Endothal 0.1 0.045 0.094 2014
Ethylene dibromide (EDB)0.00005 0.00002 0.00001 2003
Glyphosate 0.7 0.025 0.9 2007
Heptachlor 0.00001 0.00001 0.000008 1999
Heptachlor epoxide 0.00001 0.00001 0.000006 1999
Hexachlorobenzene 0.001 0.0005 0.00003 2003
Hexachlorocyclopentadiene 0.05 0.001 0.002 2014
Lindane 0.0002 0.0002 0.000032 1999 (rev2005)
Methoxychlor 0.03 0.01 0.00009 2010
Molinate 0.02 0.002 0.001 2008
Oxamyl 0.05 0.02 0.026 2009
Pentachlorophenol 0.001 0.0002 0.0003 2009
Picloram 0.5 0.001 0.5 1997
Picloram ----0.166 2015 draft
Polychlorinated biphenyls (PCBs)0.0005 0.0005 0.00009 2007
Simazine 0.004 0.001 0.004 2001
2,4,5-TP (Silvex)0.05 0.001 0.003 2014
2,3,7,8-TCDD (dioxin) 3x10 -8 5x10 -9 5x10 -11 2010
Thiobencarb 0.07 0.001 0.07 2000
Thiobencarb ----0.042 2015 draft
Toxaphene 0.003 0.001 0.00003 2003
(b) Non-Volatile Synthetic Organic Chemicals (SOCs)
Exhibit B
4 of 4
Constituent MCL DLR PHG or (MCLG)Date of PHG
Total Trihalomethanes 0.080 --
Total Trihalomethanes ----0.0008 2010 draft
Bromodichloromethane --0.0010 (zero)--
Bromoform --0.0010 (zero)--
Chloroform --0.0010 (0.07)--
Dibromochloromethane --0.0010 (0.06)--
Haloacetic Acids (five) (HAA5)0.060 ------
Monochloroacetic Acid --0.0020 (0.07)--
Dichloroacetic Adic --0.0010 (zero)--
Trichloroacetic Acid --0.0010 (0.02)--
Monobromoacetic Acid --0.0010 ----
Dibromoacetic Acid --0.0010 ----
Bromate 0.010 0.0050 or 0.0010 a 0.0001 2009
Chlorite 1.0 0.020 0.05 2009
Coliform % positive samples %5 (zero)
Cryptosporidium**TT (zero)
Giardia lamblia**TT (zero)
Legionella**TT (zero)
Viruses**TT (zero)
N-Nitrosodimethylamine (NDMA)----0.000003 2006
1,2,3-Trichloropropane --0.000005 0.0000007 2009
Notes:
** Surface water treatment = TT
Chemicals with PHGs established in response to DDW requests. These are not currently regulated drinking water
contaminants.
a DDW will maintain a 0.0050 mg/L DLR for bromate to accommodate laboratories that are using EPA Method 300.1. However,
laboratories using EPA Methods 317.0 Revision 2.0, 321.8, or 326.0 must meet a 0.0010 mg/L MRL for bromate and should
report results with a DLR of 0.0010 mg/L per Federal requirements.
*OEHHA's review of this chemical during the year indicated (rev20XX) resulted in no change in the PHG
Chemicals with MCLs in 22 CCR §64533 —Disinfection Byproducts
Microbiological Contaminants (TT = Treatment Technique)
Office of Environmental Health Hazard Assessment Page 1
Water Toxicology Section
February 2016
Health Risk Information for
Public Health Goal Exceedance Reports
Prepared by
Office of Environmental Health Hazard Assessment
California Environmental Protection Agency
February 20 1 6
Under the Calderon -Sher Safe Drinking Water Act of 1996 (the Act), w ater utilities are
required to prepare a report every three years for contaminants that exceed public
health goals (PHGs) (Health and Safety Code Section 116470 (b)(2)). The numerical
health risk for a contaminant is to be presented with the category of h ealth risk, along
with a plainly worded description of these terms. The cancer health risk is to be
calculated at the PHG and at the California maximum contaminant level (MCL). This
report is prepared by the Office of Environmental Health Hazard Assessme nt (OEHHA )
to assist the water utilities in meeting their requirements.
PHGs are concentrations of contaminants in drinking water that pose no significant
health risk if consumed for a lifetime . PHGs are developed and p ublished by OEHHA
(Health and Safety Code Section 116365) using current risk assessment principles,
pra ctices and methods .
Numerical health risks . Table 1 present s health risk categorie s and cancer risk values
for chemical contaminants in drinking water that have PHGs .
The Act requires that OEHHA publish PHGs based on health risk assessments using
the most current scientific methods. As defined in statute, PHGs for non -carcinogenic
chemicals in drinking water are set at a concentration “at which no known or anticipated
adverse health ef fects will occur, with an adequate margin of safety.” For carcinogens ,
PHGs are set at a concentration that “does not pose any significant risk to health.”
PHGs provide one basis for revising MCLs, along with cost and technological feasibility.
OEHHA ha s been publishing PHGs since 1997 and the entire list published to date is
shown in Table 1.
Office of Environmental Health Hazard Assessment Page 2
Water Toxicology Section
February 2016
Table 2 presents health risk information for contaminants that do not have PHGs but
have state or federal regulatory standards. The Act requires that , for chemica l
contaminants with California MCLs that do not yet have PHGs, water utilities use the
federal maximum contaminant level goal (MCLG) for the purpose of complying with the
requirement of public notification. MCLGs, like PHGs, are strictly health based and
include a margin of safety. One difference, however, is that the MCLGs for carcinogens
are set at zero because the US Environmental Protection Agency (US EPA) assumes
there is no absolutely safe level of exposure to such chemicals . PHGs, on the other
han d, are set at a level considered to pose no significant risk of cancer; this is usually a
no more than one -in -one -million excess cancer risk (1 10 -6 ) level for a lifetime of
exposure. I n Table 2 , t he cancer risks shown are based on the US EPA’s evaluation s.
For more information on health risks: The adverse health effects for each chemical
with a PHG are summarized in a PHG technical support document. These documents
are available on the OEHHA Web site (http://www.o ehha.ca.gov ). Also, technical fact
sheets on most of the chemicals having federal MCLs can be found at
http://www.epa.gov/your -drinking -water/table -regulate d -drinking -water -contaminants .
Office of Environmental Health Hazard Assessment Page 3
Water Toxicology Section
February 2016
Table 1: Health Risk Categories and Cancer Risk Values for Chemicals
with California Public Health Goals (PHGs)
Chemical Health Risk Category 1
California
PHG
(mg/L)2
Cancer
Risk 3
at the
PHG
California
MCL 4
(mg/L)
Canc er
Risk at the
California
MCL
Alachlor c arcinogenicity
(causes cancer)
0.004 NA 5 0.002 NA
Aluminum neurotoxic ity and
immunotoxicity
(harms the nervous and
immune system s )
0.6 NA 1 NA
Antimony digestive system toxicity
(cause s vomiting )
0.02 NA 0.006 NA
Arsenic c arcinogenicity
(causes cancer)
0.000004
(4 × 10 -6 )
1 10 -6
(one per
million)
0.0 1 2.5 10 -3
(2.5 per
thousan d)
Asbestos c arcinogenicity
(causes cancer)
7 MFL 6
(fibers
>10
microns in
length)
1 10 -6 7 MFL
(fibers
>10
microns in
length)
1 10 -6
(one per
million)
Atrazine c arcinogenicity
(causes cancer)
0.00015 1 10 -6 0.001 7 10 -6
(seven per
million)
1 B ased on the OEHHA PHG technical support document unless otherwise specified. The categories are
the hazard traits defined by OEHHA for California’s Toxics Information Clearinghouse (online at:
ht tp://oehha.ca.gov/multimedia/green/pdf/GC_Regtext011912.pdf ).
2 mg/L = milligrams per liter of water or parts per million (ppm)
3 Cancer Risk = Upper estimate of excess cancer risk from lifetime exposure . Actual cancer risk may be
lower or zero. 1 10 -6 means one excess cancer case per million people exposed .
4 MCL = maximum contaminant level.
5 NA = not applicable. R isk cannot be calculated. The PHG is set at a level that is believed to be without
any significant public health risk to individuals expo sed to th e chemical over a lifetime.
6 MFL = million fibers per liter of water .
Office of Environmental Health Hazard Assessment Page 4
Water Toxicology Section
February 2016
Table 1: Health Risk Categories and Cancer Risk Values for Chemicals
with California Public Health Goals (PHGs)
Chemical Health Risk Category 1
California
PHG
(mg/L)2
Cancer
Risk 3
at the
PHG
California
MCL 4
(mg/L)
Canc er
Risk at the
California
MCL
Barium cardiovascular toxicity
(causes high blood
pressure )
2 NA 1 NA
Bentazon hepatotoxicity and
digestive system toxicity
(h arms the liver ,
intestine , and causes
body weight effects 7 )
0.2 NA 0.018 NA
Benzene carcinogenicity
(causes leukemia)
0.00015 1 10 -6 0.001 7 10 -6
(seven pe r
million)
Benzo[a]pyrene c arcinogenicity
(causes cancer)
0.00000 7
(7 10 -6 )
1 10 -6 0.0002 3 10 -5
(three per
hundred
thousand)
Beryllium digestive system toxicity
(harms the stomach or
intestine )
0.001 NA 0.004 NA
Bromate c arcinogenicity
(causes cancer)
0.0001 1 10 -6 0.01 1 10 -4
(one per
ten
thousand )
Cadmium nephrotoxicity
(harms the kidney )
0.0000 4 NA 0.005 NA
Carbofuran reproductive toxicity
(harms the testis)
0.0017 NA 0.018 NA
7 Body weight effects are an indicator of general toxicity in animal studies.
Office of Environmental Health Hazard Assessment Page 5
Water Toxicology Section
February 2016
Table 1: Health Risk Categories and Cancer Risk Values for Chemicals
with California Public Health Goals (PHGs)
Chemical Health Risk Category 1
California
PHG
(mg/L)2
Cancer
Risk 3
at the
PHG
California
MCL 4
(mg/L)
Canc er
Risk at the
California
MCL
Carbon
tetrachloride
c arcinogenicity
(causes cancer)
0.0001 1 10 -6 0.0005 5 10 -6
(five per
million)
Chlordane c arcinogenicity
(caus es cancer)
0.00003 1 10 -6 0.0001 3 10 -6
(three per
million)
Chlorite hematotoxicity
(causes anemia )
neurotoxicity
(causes neurobehavioral
effec ts )
0.05 NA 1 NA
Chromium,
hexavalent
c arcinogenicity
(causes cancer)
0.00002 1 10 -6 0.01 5×10 -4
(five per
ten
thousand)
Copper digestive system toxicity
(cause s nausea,
vomiting , diarrhea )
0.3 NA 1.3 (AL 8 ) NA
Cyanide neuro toxicity
(damages nerve s)
endocrine toxicity
(affects the thyroid)
0.15 NA 0.15 NA
Dalapon nephrotoxicity
(harms the kidney )
0.79 NA 0.2 NA
8 AL = action level. The action level s for copper and lead refer to a co ncentration measured at th e tap. M uch
of the copper and lead in drinking water is derived from household plumbing (The Lead and Copper Rule,
Title 22, California Code of Regulations [CCR] section 64672.3).
Office of Environmental Health Hazard Assessment Page 6
Water Toxicology Section
February 2016
Table 1: Health Risk Categories and Cancer Risk Values for Chemicals
with California Public Health Goals (PHGs)
Chemical Health Risk Category 1
California
PHG
(mg/L)2
Cancer
Risk 3
at the
PHG
California
MCL 4
(mg/L)
Canc er
Risk at the
California
MCL
1,2 -Dibromo -3 -
chloropropane
(DBCP)
c arcinogenicity
(causes cancer)
0.0000017
(1.7x10 -6 )
1 10 -6 0.0002 1 10 -4
(one per
ten
thousand )
1,2 -Dichloro -
benzene (o -
DCB)
hepatotoxicity
(harms the liver )
0.6 NA 0.6 NA
1,4 -Dichloro -
benzene (p -
DCB)
c arcinogenicity
(causes cancer)
0.006 1 10 -6 0.005 8 10 -7
(eight per
ten million)
1,1 -Dichloro -
ethane (1,1 -
DC A)
c arcinogenicity
(causes cancer)
0.003 1 10 -6 0.005 2 10 -6
(two per
million)
1,2 -Dichloro -
ethane (1,2 -
DCA)
c arcinogenicity
(causes cancer)
0.0004 1 10 -6 0.0005 1 10 -6
(one per
million )
1,1 -Dichloro -
ethylene
(1,1 -DCE)
hepatotoxicity
(harms the liver )
0.01 NA 0.006 NA
1,2 -Dichloro -
ethylene, cis
n ephrotoxicity
(harms the kidney )
0.1 NA 0.006 NA
1,2 -Dichloro -
ethylene, trans
hepatotoxicity
(harms the liver )
0.06 NA 0.01 NA
Dichloromethane
(methylene
chloride)
c arcinogenicity
(causes cancer)
0.004 1 10 -6 0.005 1 10 -6
(one per
million)
2,4 -Dichloro -
phenoxyacetic
acid (2,4 -D)
hepatotoxicity and
nephrotoxicity
(harms the liver and
kidney)
0.0 2 NA 0.07 NA
Office of Environmental Health Hazard Assessment Page 7
Water Toxicology Section
February 2016
Table 1: Health Risk Categories and Cancer Risk Values for Chemicals
with California Public Health Goals (PHGs)
Chemical Health Risk Category 1
California
PHG
(mg/L)2
Cancer
Risk 3
at the
PHG
California
MCL 4
(mg/L)
Canc er
Risk at the
California
MCL
1,2 -Dichloro -
propane
(propylene
dichloride)
c arcinogenicity
(causes cancer)
0.0005 1 10 -6 0.005 1 10 -5
(one per
hundred
thousand )
1,3 -Dichloro -
propene
(Telone II )
c arcinogenicity
(causes cancer)
0.0002 1 10 -6 0.0005 2 10 -6
(two per
million)
D i(2 -ethylhexyl)
adipate (DEHA)
developmental toxicity
(disrupt s development)
0.2 NA 0.4 NA
Diethylhexyl -
phthalate
(DEHP)
c arcinogenicity
(causes cancer)
0.012 1 10 -6 0.004 3 10 -7
(three pe r
ten million)
Dinoseb reproductive toxicity
(harms the uterus and
testis)
0.014 NA 0.007 NA
Dioxin (2,3,7,8 -
TCDD)
c arcinogenicity
(causes cancer)
5 10 -11 1 10 -6 3 10 -8 6 10 -4
(s ix per ten
thousand)
Diquat ocular toxicity
(harms the eye)
developmental toxicity
(causes malformation)
0.015 NA 0.02 NA
Endothall digestive system toxicity
(harms the stomach or
intestine )
0.094 NA 0.1 NA
Endrin hepatotoxicity
(ha rms the liver )
neurotoxicity
(causes convulsions)
0.0018 NA 0.002 NA
Office of Environmental Health Hazard Assessment Page 8
Water Toxicology Section
February 2016
Table 1: Health Risk Categories and Cancer Risk Values for Chemicals
with California Public Health Goals (PHGs)
Chemical Health Risk Category 1
California
PHG
(mg/L)2
Cancer
Risk 3
at the
PHG
California
MCL 4
(mg/L)
Canc er
Risk at the
California
MCL
Ethylbenzene
(phenylethane)
hepatotoxicity
(harms the liver )
0.3 NA 0.3 NA
Ethylene
dibromide
c arcinogenicity
(causes cancer)
0.00001 1 10 -6 0.00005 5 10 -6
(five per
million)
Fluoride musculoskeletal toxicity
(causes tooth mottling)
1 N A 2 NA
Glyphosate nephrotoxicity
(harms the kidney )
0.9 NA 0.7 NA
Heptachlor c arcinogenicity
(causes cancer)
0.000 008
(8×10 -6 )
1 10 -6 0.00001 1 10 -6
(one per
million)
Heptachlor
epoxide
c arcinogenicity
(causes cancer)
0.000006
(6×10 -6 )
1 10 -6 0.00001 2 10 -6
(two per
million)
Hexachloroben -
zene
c arcinogenicity
(causes cancer)
0.00003 1 10 -6 0.001 3 10 -5
(three per
hundred
thousand)
Hexachloro -
cyclo pentad iene
(H CCPD )
digestive system toxicity
(causes stomach
lesions)
0.002 NA 0.05 NA
Lead developmental
neuro toxicity
(causes neurobehavioral
effects in children )
cardiovascular t oxicity
(cause s high blood
pressure )
carcinogenicity
(causes cancer)
0.00 0 2 <1 10 -6
(PHG is
not based
on this
effect)
0.015
(AL 8 )
2 10 -6
(two per
million)
Office of Environmental Health Hazard Assessment Page 9
Water Toxicology Section
February 2016
Table 1: Health Risk Categories and Cancer Risk Values for Chemicals
with California Public Health Goals (PHGs)
Chemical Health Risk Category 1
California
PHG
(mg/L)2
Cancer
Risk 3
at the
PHG
California
MCL 4
(mg/L)
Canc er
Risk at the
California
MCL
Lindane
(-BHC)
c arcinogenici ty
(causes cancer)
0.000032 1 10 -6 0.0002 6 10 -6
(six per
million)
Mercury
(inorganic)
nephrotoxicity
(harms the kidney )
0.0012 NA 0.002 NA
Methoxychlor endocrine toxicity
(causes hormone
effects)
0.00009 NA 0.03 NA
Methyl tertiary -
butyl ether
(MTBE)
c arcinogenicity
(causes cancer)
0.013 1 10 -6 0.013 1 10 -6
(one per
million)
Molinate c arcinogenicity
(causes cancer)
0.001 1 10 -6 0.02 2 10 -5
(two per
hundred
thousand)
Monochloro -
ben zene
(chlorobenzene)
nephrotoxicity
(harms the kidney)
0.07 NA 0.07 NA
Nickel developmental toxicity
(causes increased
neonatal deaths)
0.012 NA 0.1 NA
Nitrate h ematotoxicity
(causes
methemoglobinemia)
45 as
nitrate
NA 10 as
nitrogen
(=45 as
nitrate)
NA
Nitrite hematotoxicity
(c auses
methemoglobinemia)
1 as
nitrogen
N A 1 as
nitrogen
NA
Office of Environmental Health Hazard Assessment Page 10
Water Toxicology Section
February 2016
Table 1: Health Risk Categories and Cancer Risk Values for Chemicals
with California Public Health Goals (PHGs)
Chemical Health Risk Category 1
California
PHG
(mg/L)2
Cancer
Risk 3
at the
PHG
California
MCL 4
(mg/L)
Canc er
Risk at the
California
MCL
Nitrate and
Nitrite
hematotoxicity
(causes
methemoglobinemia)
10 as
nitrogen
NA 10 as
nitrogen
NA
N -nitroso -
dimethyl -amine
(NDMA)
c arcinogenicity
(causes cancer)
0.000003
(3 10 -6 )
1 × 10 -6 none NA
Oxamyl general toxicity
(causes body w eight
effects )
0.0 26 N A 0.05 NA
Pentachloro -
phenol (PCP)
c arcinogenicity
(causes cancer)
0.000 3 1 10 -6 0.001 3 10 -6
(three per
million)
Perchlorate endocrine toxicity
(affects the thyroid )
developmental toxicity
(causes neurodevelop -
mental deficits )
0.001 NA 0.006 NA
Picloram hepatotoxic ity
(harms the liver )
0.5 NA 0.5 NA
Polychlorinated
biphenyls
(PCBs)
c arcinogenicity
(causes cancer)
0.00009 1 10 -6 0.0005 6 10 -6
(six per
million)
Radium -226 carcinogenicity
(causes cancer)
0.05 pCi/L 1 10 -6 5 pCi/L
(combined
Ra 226+228 )
1 10 -4
(one per
ten
thousand)
Radium -228 carcinogeni city
(causes cancer)
0.019 pCi/L 1 10 -6 5 pCi/L
(combined
Ra 226+228 )
3 10 -4
(three per
ten
thousand)
Office of Environmental Health Hazard Assessment Page 11
Water Toxicology Section
February 2016
Table 1: Health Risk Categories and Cancer Risk Values for Chemicals
with California Public Health Goals (PHGs)
Chemical Health Risk Category 1
California
PHG
(mg/L)2
Cancer
Risk 3
at the
PHG
California
MCL 4
(mg/L)
Canc er
Risk at the
California
MCL
Selenium integumentary toxicity
(causes hair loss and
nail damage )
0.03 N A 0.05 NA
Silvex (2,4,5 -TP) hepatotoxicity
(harms the liver )
0.003 NA 0.05 NA
Simazine general toxicity
(causes body weight
effects )
0.004 NA 0.004 NA
Strontium -90 carcinogenicity
(causes cancer)
0.35 pCi/L 1 × 10 -6 8 pCi/L 2 10 -5
(two per
hundred
thousand)
Styrene
(vinylbenzene)
c arcinogenicity
(causes cancer)
0.0005 1 × 10 -6 0.1 2 10 -4
(two per
ten
thousand)
1,1,2,2 -
Tetrachloro -
ethane
c arcinogenicity
(causes cancer)
0.0001 1 10 -6 0.001 1 10 -5
(one per
hundred
thousand)
Tetrachloro -
ethylene
(perchloro -
ethylene, or
PCE)
c arcinogenicity
(causes cancer)
0.00006 1 10 -6 0.005 8 10 -5
(eight per
hundred
thousand)
Thallium integumentary toxicity
(causes hair loss)
0.0001 NA 0.002 NA
Thiobencarb general toxicity
(causes body weight
effects )
hematotoxicity
(affects red blood cells )
0.07 NA 0.07 NA
Office of Environmental Health Hazard Assessment Page 12
Water Toxicology Section
February 2016
Table 1: Health Risk Categories and Cancer Risk Values for Chemicals
with California Public Health Goals (PHGs)
Chemical Health Risk Category 1
California
PHG
(mg/L)2
Cancer
Risk 3
at the
PHG
California
MCL 4
(mg/L)
Canc er
Risk at the
California
MCL
Toluene
(methylbenzene)
hepatotoxicity
(harms the liver )
endocrine toxicity
(harms th e thymus)
0.15 NA 0.15 NA
Toxaphene c arcinogenicity
(causes cancer)
0.00003 1 10 -6 0.003 1 10 -4
(one per
ten
thousand)
1,2,4 -Trichloro -
benzene
endocrine toxicity
(harms adrenal glands)
0.005 NA 0.005 NA
1,1,1 -Trichloro -
ethane
n euro toxicity
(harms the nervous
system ),
reproductive toxicity
(causes fewer offspring)
hepato toxicity
(harms the liver )
hematotoxicity
(causes blood effects)
1 NA 0.2 NA
1,1,2 -Trichloro -
ethane
c arcinogenicity
(causes cancer)
0.0003 1x10 -6 0.005 2 10 -5
(two per
hundred
thousand)
Trichloro -
ethylene (TCE)
c arcinogenicity
(causes cancer)
0.00 17 1 10 -6 0.005 3 10 -6
(three per
million)
Trichlorofluoro -
methane
(Freon 11)
accelerated mortality
(increase in early death )
1.3 NA 0.15 NA
Office of Environmental Health Hazard Assessment Page 13
Water Toxicology Section
February 2016
Table 1: Health Risk Categories and Cancer Risk Values for Chemicals
with California Public Health Goals (PHGs)
Chemical Health Risk Category 1
California
PHG
(mg/L)2
Cancer
Risk 3
at the
PHG
California
MCL 4
(mg/L)
Canc er
Risk at the
California
MCL
1,2,3 -Trichloro -
propane
(1,2,3 -TCP)
c arcinog enicity
(causes cancer)
0.0000007
(7×10 -7 )
1x10 -6 none NA
1,1,2 -Trichloro -
1,2,2 -trifluoro -
ethane
(Freon 113)
hepato toxicity
(harms the liver )
4 NA 1.2 NA
Tritium carcinogenicity
(causes cancer)
400 pCi/L 1x10 -6 20,000
pCi/L
5x10 -5
(five per
hundred
thousand)
Uranium carcinogenicity
(c auses cancer)
0.43 pCi/L 1 10 -6 20 pCi/L 5 10 -5
(five per
hundred
thousand)
Vinyl chloride c arcinogenicity
(causes cancer)
0.00005 1 10 -6 0.0005 1 10 -5
(one per
hundred
thousand)
Xylene neurotoxicity
(a ffects the senses,
mood , and motor
control)
1.8 (single
isomer or
sum of
isomers)
NA 1.75 (single
isomer or
sum of
isomers)
NA
Office of Environmental Health Hazard Assessment Page 14
Water Toxicology Section
February 2016
Table 2: Health Risk Categories and Cancer Risk Values for Chemicals
without California Public Health Goals
Chemical Health Risk Category 1
U.S. EPA
MCLG 2
(mg/L)
Cancer
Risk 3
@
MCLG
California
MCL 4
(mg/L)
Cancer
Risk @
California
MCL
Disinfection byproducts (DBPS)
C hloramines acute toxicity
(causes irritation)
digestive system toxicity
(harms the stomach)
hematotoxicity
(causes anemia)
4 5 ,6 NA 7 none NA
C hlorine acute toxicity
(causes irritation)
digestive system toxicity
(harms the stomach)
4 5 ,6 NA none NA
C hlorine dioxide hemato toxicity
(causes anemia)
neurotoxicity
(harms the nervous
system )
0.8 5 ,6 NA none NA
Disinfection byproducts: haloacetic acids (HAA5)
C hloroacetic acid general toxicity
(causes body and organ
weight changes 8 )
0.07 NA none NA
1 Health risk category based on the U.S. EPA MCLG document or California MC L document
unless otherwise specified.
2 MCLG = maximum contaminant level goal established by U.S. EPA.
3 Cancer Risk = Upper estimate of excess cancer risk from lifetime exposure . Actual cancer risk
may be lower or zero. 1 10 -6 means one excess cancer c ase per million people exposed .
4 California MCL = maximum contaminant level established by California.
5 Maximum Residual Disinfectant Level Goal, or MRDLG .
6 The federal Maximum Residual Disinfectant Level (MRDL), or highest level of disinfectant
allowed in drinking water, is the same value for this chemical.
7 NA = not available.
8 Body weight effects are an indicator of general toxicity in animal studies.
Office of Environmental Health Hazard Assessment Page 15
Water Toxicology Section
February 2016
Table 2: Health Risk Categories and Cancer Risk Values for Chemicals
without California Public Health Goals
Chemical Health Risk Category 1
U.S. EPA
MCLG 2
(mg/L)
Cancer
Risk 3
@
MCLG
California
MCL 4
(mg/L)
Cancer
Risk @
California
MCL
D ichloroacetic
acid
c arcinogenicity
(causes cancer)
0 0 none NA
T richloroacetic
acid
hepatotoxicity
(harms the liver )
0.02 0 none NA
B romoacetic acid NA none NA none NA
D ibromoacetic
acid
NA none NA none NA
T otal haloacetic
acids
c arcinogenicity
(causes cancer)
none NA 0.06 NA
Disinf ection byproducts: trihalomethanes (THM s )
B romodichloro -
methane (BDCM)
c arcinogenicity
(causes cancer)
0 0 none NA
B romoform c arcinogenicity
(causes cancer)
0 0 none NA
C hloroform hepatotoxicity and
nephrotoxicity
(harms the liver and
kidney)
0.07 NA none NA
D ibromo -
chloromethane
(DBCM)
h epatotoxicity ,
nephrotoxicity , and
neurotoxicity
(harms the liver, kidn ey,
and nervous system)
0.06 NA none NA
T otal
trihalomethanes
(sum of BDCM,
bromoform,
chloroform and
DBCM)
c arcinogenicity
(causes cancer),
hepatotoxicity,
nephrotoxicity, and
neurotoxicity
(harms the liver, kidney,
and nervous system)
none NA 0.08 NA
Office of Environmental Health Hazard Assessment Page 16
Water Toxicology Section
February 2016
Table 2: Health Risk Categories and Cancer Risk Values for Chemicals
without California Public Health Goals
Chemical Health Risk Category 1
U .S. EPA
MCLG 2
(mg/L)
Cancer
Risk 3
@
MCLG
California
MCL 4
(mg/L)
Cancer
Risk @
California
MCL
Radionuclides
G ross alpha
particles 9
carcinogenicity
(causes cancer)
0 (210 Po
included)
0 15 pCi/L 10
(includes
226 Ra but
not radon
and
uranium)
up to 1x10 -3
(for 210 Po,
the most
potent
alpha
emitter
B eta particles and
photon emitters 9
carcinogenicity
(causes cancer)
0 (210 Pb
included)
0 50 pCi/L
(judged
equiv. to 4
mrem/yr)
up to 2x10 -3
(for 210 Pb,
the most
potent
beta -
emitter)
9 MCLs for gross alpha and beta particles are screening standards for a group of radionuclides.
Co rresponding PHGs were not developed for gross alpha and beta particles. S ee the OEHHA
memoranda discussing the cancer risks at these MCLs at
http://oehha.studio -weeren.com/media/downloads/water/chemicals/phg/grossalphahealth.pdf .
10 pCi/L = picocuries per liter of water.
KEY TO ABBREVIATIONS
CITY OF SANTA MONICA PUBLIC WORKS/WATER RESOURCES DIVISION
Summary of Results for Primary Drinking Water Standards for 2013
Primary Drinking Water Standards = MCLs, MRDLs and treatment techniques
for contaminants that affect health along with their monitoring and reporting
requirements, and water treatment requirements.
PHG = Public Health Goal, or the level of a contaminant in drinking water below
which there is no known or expected risk to health. PHGs are set by the California
Environmental Protection Agency.
MCLG = Maximum Contaminant Level Goal, or the level of a contaminant in drinking
water below which there is no known or expected risk to health. MCLGs are set by
the U.S. Environmental Protection Agency.
MCL = Maximum Contaminant Level, or the highest level of a contaminant that is
allowed in drinking water. Primary MCLs are set as close to the PHGs (or MCLGs) as
is economically and technologically feasible.
MRDLG = Maximum Residual Disinfectant Level Goal, or the level of a drinking water
disinfectant below which there is no known or expected risk to health. They do not
reflect the benefits of the use of disinfectants to control microbials.
MRDL = Maximum Residual Disinfectant Level, or the highest level of a disinfectant
allowed in drinking water. There is convincing evidence that addition of a
disinfectant is necessary for control of microbial contaminants.
LRAA = Locational Running Annual Average. The running annual average is based on
monitoring location.
AL = Action Level, or the concentration of a contaminant which, when exceeded,
triggers treatment or other requirements which a water system must follow.
NS = No Standard
ND = Monitored for but Not Detected
NTU = Nephelometric Turbidity Units - used to measure cloudiness of drinking water.
ppb = parts per billion, or micrograms per liter (µg/l)
ppm = parts per million, or milligrams per liter (mg/l)
pCi/l =picocuries per liter
* = secondary standard
(a) = SM W ell#1 is pumped into a transmission line, is blended with Imported Surface
Water and enters the system at 19th St. & Idaho Ave.
(b) = W e are not required to test for every parameter each year. If indicated, data is
from a previous year.
(c) = T wo consecutive Total Coliform-positive samples, one of which contains Fecal
Coliform/E. Coli constitutes an acute MCL violation.
No violations occurred for 2013.
(d) = The MCL has been replaced with a treatment technique requiring agencies
to optimize corrosion control. Results given are from first draw, at-the-tap
monitoring performed every three years.
(e) = T oluene is monitored weekly at the Arcadia Plant. In 2013, very low levels of
toluene were detected two times after the completion of reservoir roof repairs in
June 2013. The detections were traced to a glue used in the repair process.
FOR ADDITIONAL WATER QUALITY QUESTIONS, CONTACT M. CARDENAS, ASSISTANT MANAGER FOR WATER PRODUCTION AND TREATMENT AT 310-826-6712
LOCAL IMPORTED IMPORTED Dates Meets MAJOR SOURCES
PHG/ State WELL W ATER SM WELL #1(a) SURF ACE WATER SURF ACE WATER Sampled Std IN DRINKING W ATER
Parameter [MCLG]/ MCL/ Arcadia Plant W eymouth Plant Jensen Plant if other
{MRDLG} {MRDL} A verage Range A verage Range A verage Range A verage Range than 2013(b)
PRIMARY DRINKING WATER STANDARDS (MANDATORY HEALTH-RELATED STANDARDS)
Clarity
Maximum Turbidity (NTU) NS 95% <0.3 N/A N/A N/A N/A 0.05 100% <0.3 0.1 100% <0.3 Y Soil runoff
Microbiological
Total Coliform Bacteria [0] 5% City-wide Maximum: 0 Positive Samples Y Naturally present in the environment
(% positive samples/month)
Fecal Coliform/E. Coli [0] (c) City-wide Maximum: 0 Positive Samples Y Human and animal fecal waste
Organic Chemical
Methyl tert-Butyl Ether (MTBE) (ppb) 13 13(5*) ND ND ND ND ND ND ND ND Y Leaking underground storage tanks
Trichloroethylene (ppb) 1.7 5 ND ND ND ND ND ND ND ND Y Discharge from metal degreasing sites
Toluene (ppb) (e) 150 150 ND ND - 1.8 ND ND ND ND ND ND Y Discharge from petroleum based products
Disinfection
Byproducts & Residuals
Total Trihalomethanes (ppb) NS 80 City-wide LRAA: 16 Range: 1 - 52 Y By-product of drinking water chlorination
Haloacetic Acids (ppb) NS 60 City-wide LRAA: 5 Range: ND - 18 Y By-product of drinking water chlorination
Total Chlorine/Chloramines (ppm) {4} {4} City-wide A verage: 1.4 Range: 0.2 - 2.4 Y Drinking water disinfectant added for treatment
Bromate (ppb) 0.1 10 N/A N/A N/A N/A N/A N/A 7.6 3.9 - 13 Y By-product of drinking water ozonation
Inorganic Chemicals
Aluminum (ppm) 0.6 1 (0.2*) ND ND ND ND 0.14 0.1 - 0.22 0.10 0.07 - 0.11 Y Erosion of natural deposits; used in water treatment process
Arsenic (ppb) 0.004 10 ND ND ND ND ND ND ND ND Y Erosion of natural deposits
Barium (ppm) 2 1 0 .02 0.02 0 .09 0 .09 N D N D N D N D Y Discharge from oil and metal industries; Erosion of natural deposits
Copper (d) (ppm) 0.3 A L=1.3 (1.0*) City-wide 90th percentile: 0.13 0 sites out of 33 exceeded the AL Y Corrosion of household plumbing systems
Fluoride After Treatment (ppm) 1 2 Control Range 0.7 - 1.3 City-wide Range 0.6 - 1.0 Y W ater additive for dental health
Lead (d) (ppb) 0.2 AL=15 City-wide 90th percentile: 2.8 0 site out of 34 exceeded the AL Y Corrosion of household plumbing systems
Nitrate (as N) (ppm) 10 10 0.8 0.5 - 1.1 3.7 3.6 - 3.8 0.5 0.5 .05 0.5 Y Runoff from fertilizer use; Leaching from sewage;
Erosion of natural deposits
Perchlorate (ppb) 6 6 ND ND ND ND ND ND ND ND Y Industrial waste discharge
Radionuclides
Alpha emitters (pCi/l) [0] 15 ND ND ND ND ND ND - 3 ND ND 2011 Y Erosion of natural deposits
Beta/photon emitters (pCi/l) [0] 50 N/A N/A N/A N/A 4 ND - 6 ND ND 2011 Y Decay of natural and man-made deposits
Combined Radium (pCi/l) [0] 5 ND ND ND ND ND ND ND ND 2011 Y Erosion of natural deposits
Uranium (pCi/l) 0.43 20 1.8 1.5 - 2.0 ND ND 2 1 - 2 1 ND - 2 2011 Y Erosion of natural deposits
KEY TO ABBREVIATIONS
CITY OF SANTA MONICA PUBLIC WORKS/WATER RESOURCES DIVISION
Summary of Results for Primary Drinking Water Standards for 2014
Primary Drinking Water Standards = MCLs, MRDLs and treatment techniques
for contaminants that affect health along with their monitoring and reporting
requirements, and water treatment requirements.
PHG = Public Health Goal, or the level of a contaminant in drinking water below
which there is no known or expected risk to health. PHGs are set by the California
Environmental Protection Agency.
MCLG = Maximum Contaminant Level Goal, or the level of a contaminant in drinking
water below which there is no known or expected risk to health. MCLGs are set by
the U.S. Environmental Protection Agency.
MCL = Maximum Contaminant Level, or the highest level of a contaminant that is
allowed in drinking water. Primary MCLs are set as close to the PHGs (or MCLGs) as
is economically and technologically feasible.
MRDLG = Maximum Residual Disinfectant Level Goal, or the level of a drinking water
disinfectant below which there is no known or expected risk to health. They do not
reflect the benefits of the use of disinfectants to control microbials.
MRDL = Maximum Residual Disinfectant Level, or the highest level of a disinfectant
allowed in drinking water. There is convincing evidence that addition of a
disinfectant is necessary for control of microbial contaminants.
LRAA = Locational Running Annual Average. The running annual average is based on
monitoring location.
AL = Action Level, or the concentration of a contaminant which, when exceeded,
triggers treatment or other requirements which a water system must follow.
N/A = Not Applicable
NS = No Standard
ND = Monitored for but Not Detected
NTU = Nephelometric Turbidity Units - used to measure cloudiness of drinking water.
ppb = parts per billion, or micrograms per liter (µg/l)
ppm = parts per million, or milligrams per liter (mg/l)
pCi/l =picocuries per liter
* = secondary standard
(a) = SM W ell#1 is pumped into a transmission line, is blended with Imported Surface
Water and enters the system at 19th St. & Idaho Ave.
(b) = The City is not required to test for every parameter each year . If indicated, data is
from a previous year.
(c) = T wo consecutive Total Coliform-positive samples, one of which contains Fecal
Coliform/E. Coli constitutes an acute MCL violation.
No violations occurred for 2014.
(d) = The MCL has been replaced with a treatment technique requiring agencies
to optimize corrosion control. Results given are from first draw, at-the-tap
monitoring performed every three years.
FOR ADDITIONAL WATER QUALITY QUESTIONS, CONTACT
M. CARDENAS, ASSISTANT MANAGER FOR WATER PRODUCTION
AND TREATMENT AT 310-434-2672
LOCAL IMPORTED IMPORTED Dates Meets MAJOR SOURCES
PHG/ State WELL W ATER SM WELL #1(a) SURF ACE WATER SURF ACE WATER Sampled Std IN DRINKING W ATER
Parameter [MCLG]/ MCL/ Arcadia Plant W eymouth Plant Jensen Plant if other
{MRDLG} {MRDL} A verage Range A verage Range A verage Range A verage Range than 2014(b)
PRIMARY DRINKING WATER STANDARDS (MANDATORY HEALTH-RELATED STANDARDS)
Clarity
Maximum Turbidity (NTU) NS 95% < 0.3 N/A N/A N/A N/A 0.03 100% ≤ 0.3 0.06 100% ≤ 0.3 Y Soil runoff
Microbiological
Total Coliform Bacteria [0] 5% City-wide Maximum: 0 Positive Samples Y Naturally present in the environment
(% positive samples/month)
Fecal Coliform/E. Coli [0] (c) City-wide Maximum: 0 Positive Samples Y Human and animal fecal waste
Organic Chemical
Methyl tert-Butyl Ether (MTBE) (ppb) 13 13(5*) ND ND ND ND ND ND ND ND Y Leaking underground storage tanks
Trichloroethylene (ppb) 1.7 5 ND ND - 0.6 ND ND ND ND ND ND Y Discharge from metal degreasing sites
Disinfection
Byproducts & Residuals
Total Trihalomethanes (ppb) NS 80 City-wide LRA A: 16 Range: 4 - 55 Y By-product of drinking water chlorination
Haloacetic Acids (ppb) NS 60 City-wide LRAA: 2 Range: ND - 9 Y By-product of drinking water chlorination
Total Chlorine/Chloramines (ppm) {4} {4} City-wide A verage: 1.2 Range: 0.2 - 2.4 Y Drinking water disinfectant added for treatment
Bromate (ppb) 0.1 10 N/A N/A N/A N/A N/A N/A 7.8 4.4 - 13 Y By-product of drinking water ozonation
Inorganic Chemicals
Aluminum (ppm) 0.6 1 (0.2*) ND ND ND ND 0.14 0.07 - 0.23 0.08 ND - 0.11 Y Erosion of natural deposits; used in water treatment process
Arsenic (ppb) 0.004 10 ND ND 1.0 1.0 ND ND 2.2 2.2 Y Erosion of natural deposits
Barium (ppm) 2 1 0 .02 0.02 0 .05 0 .05 0 .11 0 .11 N D N D Y Discharge from oil and metal industries; Erosion of natural deposits
Chromium 6 (ppb) 0.02 10 ND ND 1.6 1.6 ND ND ND ND Y Naturally occuring; industrial waste discharge
Copper (d) (ppm) 0.3 A L=1.3 (1.0*) City-wide, 90th percentile: 0.13 0 sites out of 34 exceeded the AL 2013 Y Corrosion of household plumbing systems
Fluoride After Treatment (ppm) 1 2 Control Range: 0.77.3 City-wide Range: 0.6 - 1.0 Y W ater additive for dental health
Lead (d) (ppb) 0.2 AL=15 City-wide 90th percentile: 2.8 0 site out of 34 exceeded the AL 2013 Y Corrosion of household plumbing systems
Nitrate (as N) (ppm) 10 10 0.8 0.7 - 1.2 3.3 3.2 - 3.4 ND ND ND ND Y Runoff from fertilizer use; leaching from sewage;
Perchlorate (ppb) 6 6 ND ND ND ND ND ND ND ND Y Industrial waste discharge
Radionuclides
Alpha emitters (pCi/l) [0] 15 2 ND - 3 ND ND ND ND - 4 3 ND - 5 Y Erosion of natural deposits
Beta/photon emitters (pCi/l) [0] 50 N/A N/A N/A N/A 5 4 - 6 ND ND - 5 Y Decay of natural and man-made deposits
Combined Radium (pCi/l) [0] 5 ND ND ND ND ND ND ND ND Y Erosion of natural deposits
Uranium (pCi/l) 0.43 20 1.7 1.7 0.8 0.8 3 2 - 3 2 2 - 3 Y Erosion of natural deposits
City-wide Maximum: 0 Positive Samples
City-wide Maximum: 0 Positive Samples
City-wide LRAA: 16 Range: 4 - 55
City-wide LRAA: 2 Range: ND - 9
City-wide Average: 1.2 Range: 0.2 - 2.4
City-wide, 90th percentile: 0.13 0 sites out of 34 exceeded the AL
Control Range: 0.7 - 1.3 Citywide Range: 0.6 - 1.0
City-wide, 90th percentile: 2.8 0 sites out of 34 exceeded the AL
KEY TO ABBREVIATIONS
CITY OF SANTA MONICA PUBLIC WORKS/WATER RESOURCES DIVISION
Summary of Results for Primary Drinking Water Standards for 2015
Primary Drinking Water Standards = MCLs, MRDLs and treatment techniques
for contaminants that affect health along with their monitoring and reporting
requirements, and water treatment requirements.
PHG = Public Health Goal, or the level of a contaminant in drinking water below
which there is no known or expected risk to health. PHGs are set by the California
Environmental Protection Agency.
MCLG = Maximum Contaminant Level Goal, or the level of a contaminant in drinking
water below which there is no known or expected risk to health. MCLGs are set by
the U.S. Environmental Protection Agency.
MCL = Maximum Contaminant Level, or the highest level of a contaminant that is
allowed in drinking water. Primary MCLs are set as close to the PHGs (or MCLGs) as
is economically and technologically feasible.
MRDLG = Maximum Residual Disinfectant Level Goal, or the level of a drinking water
disinfectant below which there is no known or expected risk to health. They do not
reflect the benefits of the use of disinfectants to control microbials.
MRDL = Maximum Residual Disinfectant Level, or the highest level of a disinfectant
allowed in drinking water. There is convincing evidence that addition of a
disinfectant is necessary for control of microbial contaminants.
LRAA = Locational Running Annual Average. The running annual average is based on
monitoring location.
AL = Action Level, or the concentration of a contaminant which, when exceeded,
triggers treatment or other requirements which a water system must follow.
N/A = Not Applicable
NS = No Standard
ND = Monitored for but Not Detected
NTU = Nephelometric Turbidity Units - used to measure cloudiness of drinking water.
ppb = parts per billion, or micrograms per liter (µg/l)
ppm = parts per million, or milligrams per liter (mg/l)
pCi/l =picocuries per liter
* = secondary standard
(a) = SM Well#1 is pumped into a transmission line, is blended with Imported Surface
Water and enters the system at 19th St. & Idaho Ave.
(b) = The City is not required to test for every parameter each year. If indicated, data is
from a previous year.
(c) = Two consecutive Total Coliform-positive samples, one of which contains Fecal
Coliform/E. Coli constitutes an acute MCL violation.
No violations occurred for 2015.
(d) = The MCL has been replaced with a treatment technique requiring agencies
to optimize corrosion control. Results given are from first draw, at-the-tap
monitoring performed every three years.
FOR ADDITIONAL WATER QUALITY QUESTIONS, CONTACT
M. CARDENAS, ASSISTANT MANAGER FOR WATER PRODUCTION
AND TREATMENT AT 310-434-2672
LOCAL IMPORTED IMPORTED Dates Meets MAJOR SOURCES
PHG/ State WELL WATER SM WELL #1(a) SURFACE WATER SURFACE WATER Sampled Std IN DRINKING WATER
Parameter [MCLG]/ MCL/ Arcadia Plant Weymouth Plant Jensen Plant if other
{MRDLG} {MRDL} Average Range Average Range Average Range Average Range than 2015(b)
PRIMARY DRINKING WATER STANDARDS (MANDATORY HEALTH-RELATED STANDARDS)
Clarity
Maximum Turbidity (NTU) NS 95% < 0.3 N/A N/A N/A N/A 0.05 100% ≤ 0.3 0.09 100% ≤ 0.3 Y Soil runoff
Microbiological
Total Coliform Bacteria [0] 5% City-wide Maximum: 0 Positive Samples Y Naturally present in the environment
(% positive samples/month)
Fecal Coliform/E. Coli [0] (c) City-wide Maximum: 0 Positive Samples Y Human and animal fecal waste
Organic Chemical
Methyl tert-Butyl Ether (MTBE) (ppb) 13 13(5*) ND ND ND ND ND ND ND ND Y Leaking underground storage tanks
Trichloroethylene (ppb) 1.7 5 0.5 ND - 0.7 ND ND ND ND ND ND Y Discharge from metal degreasing sites
Disinfection
Byproducts & Residuals
Total Trihalomethanes (ppb) NS 80 City-wide LR41A: 16 Range: 4 - 55 Y By-product of drinking water chlorination
Haloacetic Acids (ppb) NS 60 City-wide LRAA: 2 Range: ND - 9 Y By-product of drinking water chlorination
Total Chlorine/Chloramines (ppm) {4} {4} City-wide Average: 1.2 Range: 0.2 - 2.4 Y Drinking water disinfectant added for treatment
Bromate (ppb) 0.1 10 N/A N/A N/A N/A N/A N/A 8.0 1.1 - 13 Y By-product of drinking water ozonation
Inorganic Chemicals
Aluminum (ppm) 0.6 1 (0.2*) ND ND ND ND 0.16 0.09 - 0.20 ND ND - 0.08 Y Erosion of natural deposits; used in water treatment process
Arsenic (ppb) 0.004 10 ND ND 1.0 1.0 2.1 2.1 3.3 3.3 Y Erosion of natural deposits
Barium (ppm) 2 1 0.02 0.02 0.05 0.05 0.12 0.12 ND ND Y Discharge from oil and metal industries; Erosion of natural deposits
Chromium (ppb) [100] 50 0.3 0.3 - 0.4 1.7 1.6 - 1.7 ND ND ND ND Y Discharge from steel and pulp mills; natural deposits erosion
Chromium 6 (ppb) 0.02 10 0.2 0.2 1.6 1.6 ND ND ND ND Y Naturally occuring; industrial waste discharge
Copper (d) (ppm) 0.3 AL=1.3 (1.0*) 2013 Y Corrosion of household plumbing systems
Fluoride After Treatment (ppm) 1 2 Y Water additive for dental health
Lead (d) (ppb) 0.2 AL=15 City-wide 90th percentile: 2.8 0 site out of 34 exceeded the AL 2013 Y Corrosion of household plumbing systems
Nitrate (as N) (ppm) 10 10 1.0 0.7 - 1.2 3.5 3.4 - 3.8 ND ND 0.8 0.6 - 0.9 Y Runoff from fertilizer use; leaching from sewage;
Perchlorate (ppb) 1 6 ND ND ND ND ND ND ND ND Y Industrial waste discharge
Radionuclides
Alpha emitters (pCi/l) [0] 15 ND ND ND ND ND ND - 4 3 ND - 5 2014 Y Erosion of natural deposits
Beta/photon emitters (pCi/l) [0] 50 N/A N/A N/A N/A 5 4 - 6 ND ND - 5 2014 Y Decay of natural and man-made deposits
Combined Radium (pCi/l) [0] 5 ND ND ND ND ND ND ND ND 2014 Y Erosion of natural deposits
Uranium (pCi/l) 0.43 20 1.9 1.5 -2.7 0.8 0.8 3 2 - 3 2 2 - 3 2014 Y Erosion of natural deposits
City-wide Maximum: 0 Positive Samples
City-wide Maximum: 0 Positive Samples
City-wide LRAA: 41 Range: 11 - 54
City-wide LRAA: 12 Range: ND - 2-16
City-wide Average: 1.2 Range: ND - 2.6
City-wide, 90th percentile: 0.13 0 sites out of 34 exceeded the AL
Control Range: 0.7 - 1.3 Citywide Range: 0.3 - 0.9
City-wide, 90th percentile: 2.8 0 sites out of 34 exceeded the AL
Page 1 of 2
([KLELW(
Table 1
Ref erence: 2012 ACWA PHG Survey
COST ESTIMATES FOR TREATMENT TECHNOLOGIES
(INCLUDES ANNUALIZED CAPITAL AND O&M COSTS)
No.Treatment
Technology Source of Information
Estimated Unit Cost
2012 ACWA Survey
Indexed to 2015*
($/1,000 gallons
treated)
1 Ion Exchange Coachella Valley WD, for GW, to reduce Arsenic concentrations.
2011 costs.1.99
2 Ion Exchange City of Riverside Public Utilities, for GW, for Perchlorate treatment. 0.96
3 Ion Exchange
Carollo Engineers, anonymous utility, 2012 costs for treating GW
source for Nitrates. Design souce water concentration: 88 mg/L NO 3.
Design finished water concentration: 45 mg/L NO 3 . Does not include
concentrate disposal or land cost.
0.72
4 Granular
Activated Carbon
City of Riverside Public Utilities, GW sources, for TCE, DBCP (VOC,
SOC) treatment. 0.48
5 Granular
Activated Carbon
Carollo Engineers, anonymous utility, 2012 costs for treating SW
source for TTHMs. Design souce water concentration: 0.135 mg/L.
Design finished water concentration: 0.07 mg/L. Does not include
concentrate disposal or land cost.
0.34
6
Granular
Activated Carbon,
Liquid Phase
LADWP, Liquid Phase GAC treatment at Tujunga Well field. Costs
for treating 2 wells. Treament for 1,1 DCE (VOC). 2011-2012 costs.1.47
7 Reverse Osmosis
Carollo Engineers, anonymous utility, 2012 costs for treating GW
source for Nitrates. Design souce water concentration: 88 mg/L NO 3.
Design finished water concentration: 45 mg/L NO 3 . Does not include
concentrate disposal or land cost.
0.78
8 Packed Tower
Aeration
City of Monrovia, treatment to reduce TCE, PCE concentrations.
2011-12 costs.0.42
9 Ozonation+
Chemical addition
SCVWD, STWTP treatment plant includes chemical addition + ozone
generation costs to reduce THM/HAAs concentrations. 2009-2012
costs.
0.09