The Regional Monitoring Program (RMP) is SFEI’s largest program and monitors contamination in the Estuary. It provides water quality regulators with information they need to manage the Estuary effectively. The RMP is an innovative collaborative effort between SFEI, the Regional Water Quality Control Board, and the regulated discharger community. more >
Program Manager: Meg Sedlak Lead Scientist: Jay Davis
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The Regional Monitoring Program (RMP) is SFEI’s largest program and monitors contamination in the Estuary. It provides water quality regulators with information they need to manage the Estuary effectively. The RMP is an innovative collaborative effort between SFEI, the Regional Water Quality Control Board, and the regulated discharger community.
The RMP has combined shared financial support, direction, and participation by regulatory agencies and the regulated community in a model of collective responsibility. The RMP has established a climate of cooperation and a commitment to participation among a wide range of regulators, dischargers, industry representatives, non-governmental agencies, and scientists. The RMP provides an open forum for interested parties to discuss contaminant issues facing the Bay.
Stable funding has enabled the RMP to develop long-term plans. In addition Pilot and Special Studies provide an opportunity to adapt to changing management priorities and advances in scientific understanding. RMP committees and workgroups meet regularly to keep the Program efficient, focused on the highest priority issues, and to ensure that the RMP is based on sound science. The RMP has continually improved since its inception in 1993.
The RMP has produced a world-class dataset on estuarine contaminants. Monitoring performed in the RMP determines spatial patterns and long-term trends in contamination through sampling of water, sediment, bivalves, bird eggs, and fish, and evaluates toxic effects on sensitive organisms and chemical loading to the Bay. The Program combines RMP data with data from other sources to provide for comprehensive assessment of chemical contamination in the Bay.
The RMP provides information targeted at the highest priority questions faced by managers of the Bay. The RMP produces the Annual Monitoring Results which document the activities of the program each year, a summary report (Pulse of The Estuary), technical reports that document specific studies and synthesize information from diverse sources, and journal publications that disseminate RMP results to the world’s scientific community. The RMP website provides access to RMP products and links to other sources of information about water quality in San Francisco Bay.
| Attachment | Size |
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| 2011 Program Plan.pdf | 216.36 KB |
| 2011 Detailed workplan.pdf | 1.76 MB |
The overarching goal of the program is to collect data and communicate information about water quality in the San Francisco Estuary to support management decisions. The RMP, in consultation with its stakeholders, the Technical Review Committee, and the Steering Committee refined the management questions in May 2008.
This new generation of questions will guide the RMP during its next five years and set the stage for adjustments to the monitoring program, designing special studies capable of testing specific hypotheses prior to implementing management actions or revising policies, and communicating key messages to policy-makers and the public.
Many scientists at SFEI participate in the RMP to create a successful and scientifically sound program. The work at SFEI is overseen by the Technical Review Committee (TRC), the Steering Committee (SC) and five workgroups which consist of local scientists, regulators, and stakeholders and invited scientists recognized as leaders in their field. The five workgroups are:
The RMP has two major program elements:
The Status and Trends portion includes long-term monitoring of the Bay, and is relatively constant from year to year. The Pilot and Special Studies portion changes every year and has allowed the Program to adapt in response to changes in the regulatory landscape, advances in understanding of the Estuary, and a continual drive to adjust the Program to better meet its objectives. For more information, see the 2010 RMP Program Plan.
Municipal Dischargers
Burlingame Waste Water Treatment Plant
Central Contra Costa Sanitary District
Central Marin Sanitation Agency
City of Benicia
City of Calistoga
City of Palo Alto
City of Petaluma
City of Pinole/Hercules
City of Saint Helena
City and County of San Francisco
City of San Jose/Santa Clara
City of San Mateo
City of South San Francisco/San Bruno
City of Sunnyvale
Delta Diablo Sanitation District
East Bay Dischargers Authority
East Bay Municipal Utility District
Fairfield-Suisun Sewer District
Las Gallinas Valley Sanitation District
Marin County Sanitary District #5, Tiburon
Millbrae Waste Water Treatment Plant
Mountain View Sanitary District
Napa Sanitation District
Novato Sanitation District
Rodeo Sanitary District
San Francisco International Airport
Sausalito/Marin City Sanitation District
Sonoma County Water Agency
South Bayside System Authority
Town of Yountville
Union Sanitary District
Vallejo Sanitation & Flood Control District
West County Agency
Industrial Dischargers
C & H Sugar Company
Chevron Products Company
ConocoPhillips Rodeo Refinery
Crockett Cogeneration
Dow Chemical Company
General Chemical Corporation
Rhodia, Inc.
Shell Martinez Refining Company
Tesoro Golden Eagle Refinery
USS POSCO Industries
Valero Refining Company
Mirant of California
Dredgers
Alameda Reuse and Redevelopment
Arques Shipyard and Marina
Caltrans
Chevron Richmond Long Wharf
City of Benicia
City of San Rafael
Clipper Yacht Club
ConocoPhillips Company
Corinthian Yacht Club
Paradise Cay Yacht Harbor
Port of Oakland
Port of San Francisco
Richmond Yacht Club
U.S. Army Corps of Engineers
Valero Refining Co.
Stormwater
Alameda Countywide Clean Water Program
Caltrans
City and County of San Francisco
Contra Costa Clean Water Program
Fairfield-Suisun Urban Runoff Management Program
Marin County Stormwater Pollution Prevention Program
San Mateo Countywide Stormwater Pollution Prevention Program
Santa Clara Valley Urban Runoff Pollution
Vallejo Sanitation and Flood Control District
The main technical subject areas covered by the RMP are addressed by the sixworkgroups. Workgroups consist of scientists who are currently studying the Bay, invited scientists who are nationally recognized experts in their field, and federal and state regulators. Each workgroup meets two to three times a year to address issues concerning the planning and implementation of Pilot and Special Studies and relevant elements of Status and Trends monitoring.
Activities of the workgroups, and technical content of the program as a whole, are overseen by the Technical Review Committee. The Steering Committee determines the overall budget, allocates program funds, tracks progress, and provides direction to the Program from a manager's perspective.

Technical Review Committee (TRC)
Contaminant Fate Workgroup (CFWG)
Emerging Contaminants Workgroup (ECWG)
Exposure and Effects Workgroup (EEWG)
Sources, Pathways, and Loadings Workgroup (SPLWG)
Nutrients Workgroup (Nutrients)
The Steering Committee determines the overall budget, allocation of program funds, tracks progress, and provides direction to the Program from a manager’s perspective. The Steering Committee meets quarterly.
The steering committee is composed of the following organizations and representatives:
Small POTWs |
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City of Palo Alto 2501 Embarcadero Way Palo Alto, CA 94303 |
Brad Eggleston |
P (650) 329-2104 |
Medium-sized POTWs |
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| Vallejo Sanitation & Flood Control |
Daniel Tafolla |
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Large POTWs/BADA |
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| City of San Jose |
Kirsten Struve |
P (408) 277-4512
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Refiners |
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| Western States Petroleum Association |
Kevin Buchan |
P (916) 498-7755 |
Industry |
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| USS POSCO |
Dave Allen |
P (925) 439-6093 |
Cooling Water |
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| Mirant Delta |
Steve Bauman |
P (925) 779-6583 |
Stormwater Agencies |
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| BASMAA (EOA, Inc) |
Adam Olivieri |
P (510) 832-2852 |
Dredgers |
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| Bay Planning Coalition |
John Coleman |
P (415) 397-2293 |
US Army Corps of Engineers |
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| 1455 Market Street, 16th Floor |
Rob Lawrence | P (415) 503-6808
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SFB RWQCB |
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| 1515 Clay Street, #1400 |
Tom Mumley | P (510) 622-2395
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Oversight of the technical content and quality of the RMP is provided by the Technical Review Committee (TRC), which consists of technical representatives from the Regional Board and discharger groups, with technical support from SFEI staff. The Technical Review Committee meets quarterly.
The technical review committee is composed of the following organizations and individuals.
POTWs |
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EBMUD |
Antoine Chamsii |
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South Bay Dischargers |
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| EOA, Inc. |
Tom Hall |
P (408) 730-7704 |
Refiners |
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| ARCADIS U.S., Inc. |
Bridgette Deshields |
P (707) 776-0865 x17 |
Industry |
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| USS POSCO |
Dave Allen |
P (925) 439-6670 |
Stormwater Agencies |
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| EOA, Inc. |
Chris Sommers |
P (510) 832-2852 x218 |
Dredgers |
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| Port of Oakland |
John Prall |
P (510)451-5916 |
Regional Board |
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| SFB RWQCB |
Karen Taberski |
P (510) 622-2424 |
US EPA |
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75 Hawthorne St |
Luisa Valiela |
P (415)972-3400 |
San Francisco Public Utilites Commission |
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| San Francisco Public |
Rod T. Miller |
P (415) 648-6882 ext. 1275 |
City/County of San Francisco |
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| City/County of San Francisco |
Michael Kellogg |
(415) 242-2201 |
Army Corps |
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| U.S. Army Corps of Engineers |
Rob Lawrence |
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sfei.org.
The scientific advisory panel consists of internationally known experts in this field including Dr. Barbara Mahler (US Geological Survey), Dr. Eric Stein (Southern California Coastal Water Research Project), and Dr. Michael Stenstrom (University of California – Los Angeles).
Workgroup Lead: Lester McKee
At the request of the Regional Board, the RMP expanded the biological effects portion of the Status and Trends program, which at the time only monitored for aquatic and sediment toxicity. The Exposure and Effects Workgroup (EEWG) was formed with members from SFEI, USGS, AMS, the Regional Board, and other interested stakeholders. One of the purposes of the workgroup was to develop a biological effects pilot study (the Exposure and Effects Pilot Study (EEPS)) that would help address beneficial use management questions developed by the Regional Board. By building on the recommendations of other effects workgroups, reviewing existing literature related to work in the Estuary, and soliciting recommendations from the local scientific community (through a survey) the workgroup designed a five-year plan for addressing biological effects in the Bay.
The RMP’s EEPS evaluated a balanced suite of contaminant exposure and effects indicators that respond to general and specific contamination at the biochemical, cellular, individual, population, and community level. It evaluated contaminant effects and exposure in different media (on the bay floor, in the water column, and in wetlands/estuary margins), and at different spatial scales (site-specific, regionally, and estuary-wide). These initial overarching principles incorporate recommendations of the EEWG.
At the end of the five year pilot study the workgroup was incorporated into the RMP as a permanent workgroup. The EEWG continues to address the biological effects portion of the Status and Trends program and Pilot and Special Studies.
The scientific advisory panel consists of internationally known experts in this field including Dr. Michael Fry (Fish and Wildlife Service - Hawaii), Dr. Harry Ohlendorf (CH2M Hill), Dr. Dan Schlenk (University of California – Riverside), Dr. Steve Weisberg (Southern California Coastal Water Research Project), and Dr. Don Weston (University of California – Berkeley)
Workgroup Leads: Meg Sedlak and Jay Davis
The Contaminant Fate Workgroup (CFWG) occupies the niche between the Sources, Pathways, and Loadings Workgroup (SPLWG), concerned with identifying and quantifying contaminant inputs to the estuary, and the Exposure and Effects Workgroup (EEWG), concerned with their exposure and ultimate effects on (primarily higher trophic level) biota in the ecosystem. The objective of the CFWG is to improve our understanding of physical, chemical, and biological processes that redistribute and transform contaminants in the estuary, ultimately leading to exposure of biota. Although reducing new sources and loadings of contaminants to the estuary is important, processes such as the erosion, resuspension, and deposition of contaminants from the legacy of pollution in the estuary will affect the health of the ecosystem for decades to come. Through improved information on estuary processes, we aim to assist managers in directing limited resources and prioritizing actions for reducing negative impacts, both for new contaminants entering the system as well as for legacy pollutants already in the estuary. Key components towards achieving these goals include reviewing the scientific literature, summarizing the state of our current knowledge, and using quantitative conceptual models to identify and prioritize areas in which improved information would most assist in making decisions and/or setting goals for ecosystem recovery. Workgroup members peer review these products, providing comments and recommendations based on their expertise in the estuary and other ecosystems. Once data gaps are identified, the CFWG works with other regional stakeholders such as the CEP towards developing or encouraging approaches to best collect the needed information.
The scientific advisory panel consists of internationally known experts in this field including Dr. Joel Baker (University of Washington), Dr. Dave Krabbenhoft (USGS - Wisconsin Water Science Center), Dr. Keith Stolzenbach (University of California – Los Angeles) and Dr. Frank Gobas (Simon Fraser University).
Workgroup Lead: Don Yee
The purpose of the Emerging Contaminants Workgroup (ECWG) is to evaluate the presence of emerging contaminants in the estuary. Emerging contaminants are defined as chemicals that are not currently regulated and believed to potentially pose significant ecological or human health risks (e.g., pharmaceuticals, flame retardants, and perfluorinated compounds). Because these compounds are not regulated, relatively little information is available on their toxicity or their abundance in the environment and consequently the magnitude of the risks are not well known at this time.
The scientific advisory panel consists of internationally known experts in this field including Dr. Derek Muir (Environment Canada), Dr. Jennifer Field (Oregon State University), Dr. David Sedlak (University of California – Berkeley), and Dr. Lee Ferguson (University of South Carolina). RMP staff and the advisory panel are working to develop a target list of emerging contaminants; it is likely that the list will include the following compounds: triclosan (anti-bacterial), perfluorinated compounds (water/oil repellant used for a variety of applications including treatment textiles and food-grade containers), atrazine (pesticide), and nonylphenol (surfactant).
Workgroup Leads: Meg Sedlak and Susan Klosterhaus
The Status and Trends (S&T) monitoring program is composed primarily of five program elements:
Cruise reports contain the details of our sampling cruises for each year, organized by matrix. This includes schedules, sampling procedures and methodologies, details on each sample location, and further information regarding which parameters each sample is analyed for. A graphical representation of sampling sites for each year can be found at our Sampling Stations page.
Maps of RMP sampling stations are included as attachments below.
A key for the sampling stations is available here.
For more detailed information regarding sampling cruises from each year, visit our Cruise Reports page.
| Sampling Stations | ||
|---|---|---|
| 2011-2015 Sediment Target Sites | 2011-2015 Water Target Sites | 2011 - 2015 All Target Sites (.kml) |
| 2011 (JPEG) | 2011 (JPEG) | Files for Google Earth (ZIP) |
| 2012 (JPEG) | 2012 (JPEG) | |
| 2013 (JPEG) | 2013 (JPEG) | |
| 2014 (JPEG) | 2014 (JPEG) | |
| 2015 (JPEG) | 2015 (JPEG) | |
| 2011-2015 (DOC) | 2011-2015 (DOC) | |
| 2010 | 2009 | 2008 |
| All Matrices (PDF) | Water and Sediment (PDF) | Bivalve (JPEG) |
| Sediment (JPEG) | Sediment (JPEG) | Sediment (JPEG) |
| Water (JPEG) | Water (JPEG) | Water (JPEG) |
| 2007 | 2006 | 2005 |
| Sediment (JPEG) | Bivalve (JPEG) | Bivalve (JPEG) |
| Water (JPEG) | Sediment (JPEG) | Sediment (JPEG) |
| Water (JPEG) | Water (JPEG) | |
| 2004 | 2003 | 2002 |
| Bivalve (JPEG) | Bivalve (JPEG) | Bivalve (JPEG) |
| Sediment (JPEG) | Sediment (JPEG) | Sediment (JPEG) |
| Water (JPEG) | Water (JPEG) | Water (JPEG) |
| Attachment | Size |
|---|---|
| SamplingStationsKey.doc | 39 KB |
| TargetSedSites_2011-2015.doc | 998 KB |
The RMP encourages collaboration with other programs and research projects. In general, SFEI staff and contractors will collaborate to the extent that such collaboration does not adversely affect or delay RMP activities, or require additional expenditure of time or funds not previously approved by the RMP Steering Committee. RMP Participants will have priority for requests for collaboration.
Scientists from other programs may potentially accompany RMP contractors on sampling cruises to sub-sample RMP samples or collect additional samples as long as there is no interference or delay to RMP procedures, and no compromise of RMP QA procedures. Side-by-side deployment of other samplers or moorings will be considered on a case by case basis.
RMP samples can be split to provide researchers with Bay samples provided the split is surplus material to the needs of the RMP.
To participate on an RMP cruise or to obtain split samples, please submit the following information to the Program Manager, Meg Sedlak (meg@sfei.org) and the field logistics coordinator, Paul Salop at Applied Marine Sciences: explanation of the purpose of the study; how the study relates to the RMP objectives; the type of assistance requested (e.g., boat time, split sediment samples, etc.) and the affiliation of the lead researcher. Requests should be made at least three months in advance to allow analysis of potential impacts to the RMP. All requests require official, written approval by SFEI prior to sampling and the RMP retains no liability for the external study personnel or success of the study.
Principal Investigators of approved collaborative work agree to contribute a summary of project results from data gathering efforts to the RMP Annual Monitoring Results.
In exchange for offering collaboration with other researchers, SFEI requests that the researchers acknowledge this contribution in any articles published. An example acknowledgement is presented below:
“The authors would like to thank the Regional Monitoring Program for Water Quality in the San Francisco Bay (RMP) for providing assistance in the collection of these samples. .”
Information about current and completed Pilot and Special studies can be found in the specific RMP Projects pages.
Pilot and Special Studies are key to the adaptive management of the RMP. Pilot and Special Study ideas are solicited from committees and workgroups as well as the public at large. Once compiled, the ideas are evaluated by the appropriate Workgroup, requests are made for more detailed conceptual scope of works, and the Workgroup recommendations are reviewed by the Technical Review Committee (TRC) in March. The detailed work plans are presented to the TRC and the Steering Committee (SC) and decisions for inclusion in the following year's RMP are made by the committees in July.
Many study ideas originate from within the committees and workgroups of the Program. However, input from scientists from outside the Program is also strongly encouraged. Outside scientists may also end up implementing the proposed work, providing a means of broadening the scientific horizons and skills of all parties of RMP.
For data from specific Pilot and Special Studies please contact the study's principal investigators or Meg Sedlak.
Pilot and Special Studies have allowed the RMP to adapt in response to changes in the regulatory landscape, advances in understanding of the Estuary, and a continual drive to improve the program. Pilot and Special Studies have been included in the RMP every year since its inception and have lead to significant additions and refinements to the Status and Trends monitoring program. Some of the major elements added to the Status and Trends monitoring in the past 10 years include hydrography, phytoplankton, and suspended sediment dynamics and fish contamination. Below are summaries of some of the most recent past Pilot and Special Studies by year.
For additional information on previous Pilot and Special Studies see the 2003 Pulse article "Ten Years of Pilot and Special Studies: Keys to the Success of the RMP".(PDF)
High levels of PCBs and mercury have been detected in the Guadalupe River. The RWQCB, SFEI and other agencies have developed an extensive database of concentrations of contaminants in water, sediment, and fish tissues in the Guadalupe River watershed. In part based on these data, the Guadalupe River Watershed TMDL identifies fish mercury targets, bed and suspended sediment targets for runoff from mining areas, and load allocations from urban areas. The Bay Hg TMDL calls for Guadalupe River watershed load reductions of 98% and the Bay PCB TMDL calls for load reductions of >95% for urban areas. In response, managers in the Guadalupe River have already started implementing management actions to mitigate contaminant effects including experimenting with aeration in the reservoirs to reduce mercury methylation and removal of contaminated sediment from drainage lines.
The aim of this project is to begin the development of a numeric model to assist in estimating mass loads of mercury and PCBs; to extrapolate the data to determine long-term average loads for the period of extensive rainfall data collection (1973-present); and to determine the proportional sources in the watershed and refine the assumptions of the Guadalupe River Hg TMDL. Ultimately the model will be used to assess the effects of best management practices and impacts of wetland restoration (e.g., effects of South Bay Salt Pond restoration).
This multi-year project began in 2008. In 2008, a model was developed based on land use maps, precipitation, topography, and runoff. In 2009 information on sediment and contaminants will be incorporated into the model (this was not accomplished in 2008). In year two, continued testing of the model will occur and the model will be updated to include sediment transport. A draft report of the model will be prepared and distributed for review.
The Small Tributary Loading Strategy team is currently developing a list of priority questions and monitoring needs. It is anticipated that a small tributary loading study will be developed upon completion of the strategy.
The goal of this project is to develop egg thresholds for mercury. The USGS has developed a method in which a small amount of the individual egg albumen is sampled for mercury using micro-techniques. The amount of albumen is so small that the egg remains viable. The egg is then tracked to determine the success of the hatch and chick. USGS began this technique in 2007 and will build upon the information collected to date. USGS will donate in-kind services to complete this project
This is the second year of funding for a two-year project evaluating the effects of PAH-contaminated sediments on the development of juvenile flatfish. The impacts of pyrogenic PAHs (like those detected in San Francisco Bay) on juvenile flatfish development are largely unknown. In the first year, the effects of pyrogenic (higher molecular weight) PAHs on a model fish such as zebra fish are being determined. An update on the first year activities will be presented at the November Exposure and Effects workgroup meeting.
After the identification of biological endpoints with a model fish species, in the second year, the study will examine a native species. In addition, environmental sediment samples with a PAH signature similar to San Francisco Bay will be used.
The University of Michigan group led by Dr. Joel Blum is evaluating whether mercury isotopes can be used to identify sources of mercury to the aquatic foodweb. Working in conjunction with the diffusive gradient in thin film project discussed below and the small fish mercury project, these researchers will collect sediment, water, small fish and atmospheric samples from a number of Bay Area locations to ascertain whether certain sources are contributing more to the uptake of methylmercury in biota. Preliminary results from year one will be presented at the Annual Mercury meeting in February of 2009.
The Trent University group led by Dr. Holger Hintelmann is working in conjunction with the University of Michigan group and the RMP small fish project to assess the uptake of methylmercury using diffusive gradient in thin films (DGTs). This study will also assess whether DGTs can be used as a proxy for biosentinels such as small fish. Preliminary results from year one will be presented at the Annual Mercury meeting in February of 2009.
The preliminary results of the RMP pilot study evaluating perfluorinated compounds in Pacific Harbor Seals indicates that concentrations of these compounds are an order of magnitude higher in San Francisco Bay seals than those seals sampled at the reference site (Tomales Bay approximately 45 miles to the north of San Francisco Bay). This study will provide data on several of the pathways to the Bay in attempt to understand what are the causes of significant concentrations observed in San Francisco Bay biota.
San Francisco Bay and small fish will be sampled to determine the reservoir of perfluorinated compounds in the Bay and concentrations in prey animals, respectively. In addition, small fish have high site fidelity and may indicate potential source areas. Wastewater treatment facilities will be sampled as they are believed to be a potentially significant source to surface waters. Lastly, this study will collaborate with the tributary loading studies to collect information on tributary loads.
This special study will evaluate emerging contaminants from wastewater treatment facilities (e.g., pharmaceuticals, personal care products, nano-particles, and alkylphenol ethoxylates) to determine which compounds may, or may not, pose a concern for the Bay. This study will review the literature to obtain ranges of concentrations likely to be observed in effluents and evaluate these data in the context of literature values and effects thresholds. The white paper will then prioritize these contaminants and make recommendations for future monitoring projects. The scope of this project will be further refined at the October Emerging Contaminants workgroup meeting.
The Exposure and Effects Pilot Study was initiated in 2002 to understand the biological effects of the chemical contamination observed in the Estuary. This pilot study enters its last year of earmarked funding. Biological effects of contaminants have increasing become more important to regulators and regulated community (e.g. mercury TMDL which establishes thresholds for birds and fish). As a result, the RMP has expanded its monitoring program to include impacts to biota.
In 2007, the EEPS workgroup is developing a five-year plan for monitoring biota. Integral to this plan is work on avian exposure and effects and fish exposure and effects. In keeping with this five-year plan, the EEPS committee has approved the following three studies for 2008:
Mercury (Hg) and selenium (Se) are known to impair reproduction in wildlife and these contaminants can accumulate to high concentrations in waterbirds breeding in San Francisco Bay. Although Hg and Se have different mechanistic modes of action, the primary risk of each contaminant to wildlife populations is impaired reproduction. Moreover, both contaminants are toxicologically linked such that they may interact with one another in an antagonistic or synergistic fashion. Because of their toxicological relationships, individual assessments of reproductive impairment related to either contaminant may be confounded by the relationship with the other. This study will examine the interaction of Hg and Se on the reproductive success (i.e., hatchability, abandonment, and chick survival).
EEPS will fund a study evaluating the effects of PAH-contaminated sediments on the development of juvenile flatfish. The impacts of pyrogenic PAHs (like those detected in San Francisco Bay) on juvenile flatfish development are largely unknown. This is a two year study which in the first year will examine the effects of pyrogenic (higher molecular weight) PAHs on a model fish such as zebra fish. After the identification of biological endpoints with a model fish, in the second year, the study will examine a native species such as the California flat fish. In addition, environmental sediment samples with a PAH signature similar to San Francisco Bay will be used.
Small fish are a good indicator of spatial and temporal variability in contaminants in the Bay food web. This study will examine methylmercury concentrations in pelagic and benthic fish less than one-year in age. Small fish tend to have small ranges in habitat and are dominant food-source for piscivorous fish. The purpose of this study is three-fold: to provide information of the accumulation of methyl mercury into the food web; to determine the impacts of management actions on biota (e.g., restoration of wetlands in the South bay), and to provide data for food web modeling of exposure to wildlife. This study is a four-year study that began in 2005. The primary focus of this study has been mercury; however, in 2007, small fish were collected for analysis of trace organic concentrations (i.e., PCB, pesticide, and PBDEs).
High levels of PCBs and mercury have been detected in the Guadalupe River. The RWQCB, SFEI and other agencies have developed an extensive database of concentration of contaminants in water, sediment, and fish tissues in the Guadalupe River watershed. In part based on these data, the Guadalupe River Watershed TMDL identifies mercury fish targets, bed and suspended sediment targets for runoff from mining areas, and load allocations from urban areas. The Bay Hg TMDL calls for Guadalupe River watershed load reductions of 98% and the Bay PCB TMDL calls for load reductions of >95% for urban areas. In response, managers in the Guadalupe River have already started implementing management actions to mitigate contaminant effects including experimenting with aeration in the reservoirs to reduce mercury methylation and removal of contaminated sediment from drainage lines.
A wealth of information has been collecting in the Guadalupe watershed. What is currently lacking is a validated linkage between management measures and changes in watershed loading through time. Such a tool would help managers decide for example, if mass is removed from drainage lines results in an equivalent reduction in an annual load to the Bay.
The aim of this project is to begin the development of a numeric model to assist in estimating mass loads of mercury and PCBs; to extrapolate the data to determine long term average loads for the period of extensive rainfall data collection (1973-present); and to determine the proportional sources in the watershed and refine the assumptions of the Guadalupe River Hg TMDL. Ultimately the model will be used to assess the effects of best management practices and impacts of wetland restoration (e.g., effects of South Bay Salt Pond restoration). It is envisioned that this would be a multi-year study.
Suspended sediment loads to San Francisco Bay are vital for maintaining tidal marsh and mudflat habitats and delivering nutrients and organic carbon to the base of the food web. However, suspended sediments are also frequently a source of contaminants to marshes and mudflats. As a result, the TMDLs have proposed sediment targets for watersheds of 0.2 mg Hg/kg of sediment and perhaps 0.002 mg PCB / kg of sediment. The other targets include demonstration of loading trends and/or mass removed (loads avoided). In some watersheds (such as Coyote Creek), the 0.2 Hg target is already being achieved. In other watersheds such as Guadalupe River and perhaps some of the more heavily industrialized areas, the PCB and Hg targets are not met.
At this time, there are few data to determine where management actions might be most cost-effectively applied to achieve a mass loading target, a loads avoided target, or a sediment concentration target. The need for this project, as described in the draft language for the municipal regional permit (MRP), is to quantify sediment loads by watershed and to prioritize watersheds for which empirical observations should be conducted. In addition, this project would provide data for modeling the watershed and loads to the Bay.
Monitoring suspended sediment concentrations, SSC, in coastal waters and estuaries is crucial for proper ecosystem management. Such monitoring is traditionally done in-situ, with measurements representing SSC at a few discrete points in space and time. However, recent advancement of satellite remote sensing allows for synoptic views of coastal and estuarine dynamics that would otherwise be unavailable. Results are drastically altering our perceptions of coastal ocean transport processes.
This project proposes to use moderate-resolution (250m, 500m, and 1000m) MODIS satellite imagery to investigate episodic sediment transport patterns in San Francisco Bay. Development of an event-scale sediment budget has the potential to significantly improve current estimates of contaminant loading from the Delta to the Bay. It is conceptualized that such episodic contaminant loads account for a significant portion of annual contaminant loads. However, at present we know very little regarding the percent of episodic sediment and contaminant loads that remain within the Bay.
In 2007, this project identified suitable images. Funding for 2008 will be dedicated to processing the images and delineating the boundaries of the plumes.
Animal endocrine systems are highly responsive to changes in environment, both natural and anthropogenic in origin (e.g., chemical contaminants). Thyroid hormones, part of the endocrine system, are unique in that they exert physiological effects on most tissues, and their target receptors are found in all cell types. Thyroid hormones are particularly critical for the regulation of growth and development, metabolism, and brain/neural development and function. Because alterations in the thyroid endocrine system may exert broad physiological and developmental impacts, disruption of this system by anthropogenic chemicals presents a significant concern for wildlife.
Polychlorinated biphenyls (PCBs), polyhalogenated aromatic hydrocarbons (PHAHs), and polybrominated diphenyl ethers (PBDEs) have received extensive public and scientific attention in the last several years, as these types of chemicals are persistent in the environment and have ascribed endocrine-disrupting actions. Recently published experimental studies indicate that specific congeners of each class of these chemicals can cause thyroid disruption in fish. It has been most consistently observed that the thyroid plasma T4 concentrations significantly decline as part of the endocrine disrupted condition.
The objective of this work is to characterize the environment-related disruption of the thyroid endocrine system observed in Pacific staghorn sculpin and if possible shiner surfperch. In addition, chemical contaminants in individual fish will be measured to determine whether there is a correlation between contaminants and thyroid effects. The thyroid gland function will be assessed and attempts will be made to develop markers of endocrine disruption.
The RMP has put significant effort towards understanding spatial and temporal patterns in contaminant concentrations within San Francisco Bay (e.g., Greenfield et al. 2005, Connor et al. 2006, SFEI 2006b, 2006a), and the City and County of San Francisco (CCSF) has been surveying multiple locations along the San Francisco coastline since 1987 (CCSF 2006). This study will directly address a recommendation of the RMP Technical Review Committee that the Program integrate data from other programs. The goal is to compare patterns in priority contaminants (in fish, sediment, and other matrices) present within San Francisco Bay and coastline stations at the mouth of the Estuary. This study will evaluate the combined CCSF and RMP data sets to test two hypotheses of interest to the RMP: 1. Are contaminant concentrations (Hg, PCBs, PAHs and DDTs) higher in the Estuary than along the coastline? 2. Are long-term trends in contaminant concentrations similar between the Estuary and the offshore coastline?
In the last 50 years, fluorinated alkyl substances have been used extensively in a variety of commercially available products including fire-fighting foams, refrigerants, stain repellants in textiles, and coatings for paper used in contact with food products. As a result of their chemical stability and widespread use, fluorinated alkyl substances such as perfluorooctane sulfonate (PFOS) and perfluorooctanoic acid (PFOA) have been detected in marine mammals and aquatic organisms throughout the world including relatively pristine environments such as the Arctic, Southern Hemisphere and Pacific Ocean (Kannan et al. 2002). PFOS and related perfluorinated compounds have been associated with a variety of toxic effects including mortality, carcinogenity, and adverse development. The major manufacturer of PFOS, 3M Corporation, voluntarily phased out the production of PFOS in 2000 and recently the USEPA and eight manufacturers of PFOA agreed to reduce their presence in products by 95% by 2010. Nonetheless, both of these compounds continue to remain present in the environment because they are byproducts and degradation products of other perfluorinated compounds.
Preliminary data from the 2007 pilot study of seals suggests that the concentration of perfluorinated compounds, particularly PFOS, are elevated in seals. Based on the limited 2006/2007 sampling and the initial results, the EC workgroup recommended continued monitoring of these apex predators. The 2008 study will help us to determine background concentrations and the influence of age and gender on concentrations observed in seals.
Polybrominated diphenyl ethers (PBDEs) are chemicals used as flame retardants that have been incorporated into a variety of consumer products to comply with fire safety regulations. Studies conducted by a variety of research groups have revealed that the San Francisco Bay Area is experiencing exceptionally high PBDE bioaccumulation, with concentrations in harbor seals, birds, fish, and people that are among the highest ever reported (She et al. 2002; She et al. 2004; Brown et al. 2006). Environmental and human health concerns have resulted in a ban of the most toxic PBDE mixtures (Penta- and Octa-BDE) in California, which became effective in 2006. Ecological and human health concerns also exist for Deca-BDE, which is historically the PBDE mixture used in the highest volume, but the use of Deca-BDE continues unrestricted in California. Efforts to ban Deca-BDE are ongoing in several states, including California, but to date have only been successful in Washington and Maine. Despite the unrestricted use of Deca-BDE in most states and countries (with the exception of Sweden), many large international electronics companies have reportedly phased-out the use of Deca-BDE in their products (Pakalin et al. 2007). The decline in use of PBDEs will result in an increase in the use of non-PBDE flame retardant chemicals since consumer product flammability standards have not changed and a national furniture flammability standard is in development in the United States. Risk assessment reports on the potential replacement chemicals for Penta- BDE in polyurethane foam and Deca-BDE in polymeric applications in electrical and electronic equipment have been released (US EPA 2005; European Chemicals Bureau 2007). However, compared to the PBDEs, much less is known regarding the toxicity and fate of these alternative flame retardant chemicals and information on their use (e.g. volume, locations) is generally not available. Substantial data gaps exist for non-PBDE flame retardant chemicals in the San Francisco Estuary. Assessment of the current concentrations of these compounds in the Estuary will allow us to determine the risk of exposure of these chemicals to the estuarine foodweb and to humans consuming sport fish.
In 2007, the RMP will continue the Pilot Study of contaminant exposure and effects in the Bay. The 2003 RMP Program Review Panel recommended an increase in the Exposure and Effects Pilot Study (EEPS) budget and stated that biological effects research should be a priority. In response to this concern, the SC increased the funding for the EEPS budge to $200,000 per year and extend the pilot study through 2008. This budget includes funds for SFEI labor, subcontractors (e.g., analytical laboratories), and direct costs.
The study is multifaceted, and has included a variety of different exposure and effects indicators of beneficial use impairment. The purpose of EEPS is to develop suite of environmental indicators that can be incorporated into the core Status and Trends monitoring program.
Davis et al. (2000) recommended that six observation watersheds picked on the basis of land use. This long standing recommendation by the SPLWG was indorsed by the WG during 2005 and written into the SPLWG 5-year Work Plan (McKee, 2005). To-date most information on the functioning of small tributaries in the Bay Area is based on water and sediment data collected by the USGS. During WY 2003-2006, the SPLWG oversaw the 1st Small Tributaries Loading Study on the Guadalupe River (McKee et al., 2004, 2005, 2006) chosen based on recommendations by Leatherbarrow et al. (2002). During 2005, the SPLWG oversaw and small pilot reconnaissance study of small tributaries in an effort to make a decision on where to begin a 2nd Small Tributaries Loading Study. Given that historic and current industrialized areas are found mainly on the lower-rainfall Bay margin, the SPLWG decided to recommend a small industrial watershed. Through a process of voting and WG discussion, Zone 4 Line A was chosen. Study of this small 4 km2 area in industrial/commercial Hayward will provide valuable information on loads derived from small, low rainfall, but highly impervious, commercial and industrialized “storm drain watersheds” on the Bay margin. This is particularly important for updating regional TMDL estimates of Hg and PCBs loads derived from urban runoff. In addition, loadings studies will provide baseline data so that trends through time can be assessed, and provide data for models that describe biological effects in the Bay.
Pharmaceuticals such as antibiotics (e.g., erythromycin and trimethoprim), analgesics (e.g., ibuprofen and acetaminophen), antiinflammatories (e.g., diclofenac and naproxen), antidepressants (e.g., Prozac), antihypertensives (e.g., atenolol and propranolol), anticancers (e.g., paclitaxel and tamoxifen), and sexual performance enhancers (e.g., Viagra and Levitra), among other drugs, are used to treat illness, disease, and medical conditions in humans and animals. The primary pathway is ingestion followed by subsequent excretion into the municipal sewage system, while the secondary pathway is disposal of unused and outdated medications directly into the sewage system. These biologically active compounds and their metabolites are not completely removed by current wastewater treatment technologies and are often found in treated effluents and receiving waters.
The objective of this study is to evaluate the extent of the concentration levels and occurrence of pharmaceuticals in the San Francisco Bay water and in influent and effluent from two Bay area wastewater treatment plants. A total of 30 samples will be collected: ten from the South Bay and five influent and effluent samples from two wastewater treatment plants.
This study will determine concentrations of perfluorinated compounds in Pacific harbor seals (Phoca vitulina richardsi). Harbor seals are an ideal indicator species for persistent bioaccumulative contaminants in the Estuary because they are apex predators that eat a diet consisting primarily of fish. Perfluorinated compounds are of particular concern because they are very stable compounds that are not known to undergo abiotic or biotic degradation (Martin et al. 2004). In addition to perfluorinated compounds, this study will also determine concentrations of polybrominated diphenyl ethers and other flame retardants in seal blood.
Monitoring suspended sediment concentrations, SSC, in coastal waters and estuaries is crucial for proper ecosystem management. Such monitoring is traditionally conducted in-situ, with measurements representing SSC at a few discrete points in space and time. However, recent advancement of satellite remote sensing allows for synoptic views of coastal and estuarine dynamics that would otherwise be unavailable. Results are drastically altering our perceptions of coastal ocean transport processes.
This project will use moderate-resolution (250m, 500m, and 1000m) MODIS satellite imagery to investigate episodic sediment transport patterns in San Francisco Bay. Development of an event-scale sediment budget has the potential to significantly improve current estimates of contaminant loading from the Delta to the Bay. It is conceptualized that such episodic contaminant loads account for a significant portion of annual contaminant loads. However, at present we know very little regarding the percent of episodic sediment and contaminant loads that remain within the Bay.
The project includes three tasks: 1) identify MODIS images with a high percentage of coverage in the Bay corresponding to periods of high Delta flow and process these images to produce true- and false-color images showing two-dimensional sediment transport patterns and quantifying relative concentrations of suspended matter, 2) where appropriate, utilize existing edge-detection algorithms (Oram et al. 2005) to delineate the boundaries of plumes exiting the Golden Gate and estimate mass of suspended sediment within the plume, and 3) compare remote observations with in-situ USGS SSC measurements collected at Mallard Island to determine the fraction of material entering the Bay via the Delta that is lost to the Pacific Ocean during a given event.
This study monitors bioavailable mercury in three different San Francisco Bay Open water habitats at eight fixed sampling locations by using the food web to assess interannaul and spatial trends in small fish. In 2007, a new component was added to this study which involves sampling for trace organic concentrations in small fish to determine PCB, pesticide, and PBDE concentrations by collecting additional fish from shoreline areas distributed throughout the San Francisco Estuary.
The special study will focus on obtaining an improved conceptual understanding of spatial variation in the San Francisco Bay food web. Particular emphasis will be placed on the diets of white croaker and shiner surfperch, as they are important species for understanding of the bay with respect to recovery from impairment by PCB and the results of actions taken to implement the TMDL. The special study will include a combination of literature review and field dietary studies to develop a better understanding of food web transfer pathways for contaminants. It is critical to further our understanding of the diet of target species, specifically to discern between the relative contribution of water column and sediment prey items to the diet of aquatic and other wildlife in and around the Bay. This will help evaluate the relative importance of water and sediment PCBs to white croaker and shiner surfperch, and inform managers on effective implementation actions.
One pathway of pollutants to the Estuary is atmospheric deposition, which was examined in the RMP Atmospheric Deposition Pilot Study. That study was suspended after metals (including mercury) and PAH/PCB data were incorporated into the mass budget models, indicating that atmospheric deposition is not a primary source or pathway for most of these contaminants, with the exception of PAHs. The only remaining component to the study is the continued measurement of rain samples for mercury as part of the national Mercury Deposition Network (MDN) at a station at NASA Ames (MDN CA 72) through 2004, a five-year commitment made at the start of the RMP study. Pending approval by the TRC, RMP will continue data collection at this MDN station for 2006.
The continuing objectives of this monitoring are to:
In 2005, the first year of a two-year winter pilot study was conducted. Estuarine water was sampled at three historical RMP stations (i.e., Sacramento River (BG20), Yerba Buena Island (BC10), and Dumbarton Bridge (BA30)) during the 2005 winter season (February 2005). These water samples were analyzed for contaminants on the California Toxics Rule priority pollutant list.
Wet weather S&T contaminant monitoring is potentially an important element of the RMP. At the present time, the annual S&T monitoring occurs during the dry season, and seasonal variation is not captured by this sampling plan. The results from this Pilot Study will enable SFEI to evaluate the spatial and temporal trends of pollutants in the winter. Wet season monitoring results have been an important resource provided to environmental managers of Region 2 for use in NPDES permitting and the 303(d) listing processes.
A workgroup will be convened in October 2005 to discuss the winter sampling needs for 2006 and beyond. A key discussion point for this meeting will be understanding regulatory needs and assessing whether the scope of the pilot study needs to be expanded to additional sites or matrices. Changes to the scope of the Winter Pilot study will need to be discussed and approved by the TRC and SC.
In 2006, the RMP will continue the Pilot Study of contaminant exposure and effects in the Bay. The 2003 RMP Program Review Panel recommended an increase in the Exposure and Effects Pilot Study (EEPS) budget and stated that biological effects research should be a priority. In response to this concern, the SC increased the funding for the EEPS budge to $200,000 per year and extend the pilot study through 2008. This budget includes funds for SFEI labor, subcontractors (e.g., analytical laboratories), and direct costs.
The Study is multifaceted, and has included a variety of different exposure and effects indicators of beneficial use impairment. The purpose of EEPS is to develop suite of environmental indicators that can be incorporated into the core Status and Trends monitoring program.
As outlined in the Sources, Pathways, and Loadings Workgroup Report (Davis et al. 1999), large uncertainties exist with regard to loading estimates from the Sacramento and San Joaquin rivers. Analyses from this multi-year study have suggested that our previous estimates for both suspended sediment load and Hg load were high and this has greatly affected the implementation recommendations in the recently released Hg TMDL report (Johnson and Looker, 2003). The question remains as to how accurate are our estimates. The San Francisco Bay is listed (Clean Water Act 303(d)) as impaired for mercury, selenium, PCBs, and chlorinated pesticides. This study aims to address information gaps associated with loadings of these substances (with the exception of selenium) so that a better understanding of relative inputs from urban point and non-point sources, erosion and resuspension in the Bay, and the inputs from the Central Valley rivers can be developed.
Small tributaries form a major pathway for loads of contaminants that enter the Bay each year. Models developed for the Bay are highly sensitive to the magnitude of loads from small tributaries but present load estimates for this pathway lack accuracy and precision. This study will accurately measure contaminant loads from a small tributary representative of one that may contribute significant loads of sediment and associated contaminants to the Bay, help evaluate the significance of this load as a means of prioritization of further loadings studies, demonstrate a new methodology, and compare these accurate loads measurements to existing simple model estimates.
This study is part of a joint study overseen by CEP and RMP that was described under the data integration section. The joint RMP/CEP project (CEP Project 4.26) supports efforts underway to construct a mechanistic model that advances our understanding of contaminant behavior in the Bay. The project includes sampling and analysis of sediment cores from various Bay segments and wetlands along their margins that will enhance our understanding of Bay sediment processes and its influence on the distribution of associated contaminants.
Although existing models can draw upon a pool of data characterizing surface sediment concentrations in the Bay (e.g., RMP, NOAA/EMAP), there are far fewer data for characterizing pollutants at depth. Improved data are required to better quantify the pool of legacy and emerging pollutants in the Bay, verify or place bounds on certain model parameters, and test model results against field data.
The collection of sediment cores and analyses for pollutants and radioisotopes will be used to achieve the following three objectives: (1) provide a more comprehensive characterization of contamination with depth that can be used to assess future changes, (2) verify the historic loading of pollutants to the Bay and how those loads have changed in the last several decades, and (3) provide valuable data for parameterization and evaluation of the multi-box or other Bay models.
approximately 15,000 acres are slated for wetland restoration. The potential exists to inadvertently increase the risk of mercury (Hg) accumulating in South Bay fish and wildlife through hydrological modification of salt ponds as part of the South Bay Salt Pond Restoration Project (SBSPRP). The concern is that management actions will favor conversion of Hg into toxic methylmercury (MeHg) and its uptake into local food webs. The SBSPRP has initiated a two-year study to identify indicators that can be monitored.
The Regional Water Quality Control Board has developed sediment quality objectives (SQOs) that are scheduled to be promulgated in 2008. The Water Board will need an understanding of baseline conditions of benthic assemblages in the Bay which currently does not exist. To fill this data gap, it is proposed that the RMP begin studying benthic assemblages in the Bay in 2008.
Based on discussions with the TRC and the EEPS Science Advisory Panel, it is clear that there is a need to build consensus on a benthic assessment process. Key RMP staff have met with the Regional Water Quality Control Board to discuss a benthic assessment workshop. This workshop will be held in the Spring 2006.
The Air Deposition Pilot Study was suspended after metals and PAH/PCB data were incorporated into the mass budget models. The only remaining component is the measurement of rain samples for mercury to continue as part of the national Mercury Deposition Network through 2004, after which a decision will be made annually as to whether or not to continue data collection. For 2005, the TRC has elected to fund this project. The project includes SFEI staff time for sampling and trouble-shooting assistance, participation in site audits, and coordination with City of San Jose staff as necessary. The City of San Jose is providing in-kind sampling assistance, with samples being shipped to the MDN laboratory.
The RMP in 2005 will continue a Pilot Study of contaminant exposure and effects in the Bay. The Exposure and Effects Advisory Panel assembled to guide this study has recommended a narrowed focus on the following topics: fish, birds, seals, benthos, and toxicity. The 2003 RMP Program Review Panel recommended an increase in the Exposure and Effects Pilot Study (EEPS) budget and stated that biological effects research should be a priority. In response to this concern, the SC allocated $200,000 for the EEPS for 2005. This includes funds for SFEI labor, subcontractors (e.g., analytical laboratories), and grant proposal development. Also in response to the Review Panel recommendation, the SC and TRC extended the duration of the study for another two years (through 2008).
The Study is multifaceted, and has included a variety of different exposure and effects indicators of beneficial use impairment. In 2003 and 2004, EEPS work was scaled back. In 2004, indicators tested included cormorant eggs (chemical trend indicators), mercury concentrations in harbor seals (exposure and effects indicators), sediment dose-response sensitivity testing comparing laboratory and resident amphipod species, and benthic community evaluations using a multi-metric approach (effects). Diving duck samples (human health indicator) were also collected in 2004. However, due to a freezer malfunction, the samples were compromised and it was decided not to analyze these samples. In 2004 the Exposure and Effects Advisory Panel met and provided input on a conceptual framework for the study that was developed at the Panel’s request.
The EEPS will return to its full funding and activity level ($200,000) in 2005. The Exposure and Effects Workgroup will meet in early 2005 to develop a new multi-year plan. Several projects discussed by the Workgroup in the past will be considered for funding in 2005:
The primary purpose of this Pilot Study in 2005 is to comply with an NPDES permit provision for ambient water monitoring for dischargers in the San Francisco Bay area. Estuarine water will be sampled at three historical RMP stations (i.e., Sacramento River (BG20), Yerba Buena Island (BC10), and Dumbarton Bridge (BA30)) during the 2005 winter season (February 2005). These water samples will be analyzed for contaminants on the California Toxics Rule priority pollutant list.
Wet weather S&T contaminant monitoring is an important element of the RMP. At the present time, the core monitoring program, S&T, occurs during the dry season, and seasonal variation is not captured by this sampling plan. The results from this Pilot Study will enable SFEI to evaluate the importance of seasonal variation. Seasonal contaminant monitoring results have been an important resource provided to environmental managers of Region 2 for use in NPDES permitting and the 303(d) listing processes.
A workgroup will be convened in 2005 to determine additional needs for winter sampling within the RMP
As outlined in the Sources, Pathways, and Loadings Workgroup Report (Davis et al. 1999), large uncertainties exist with regard to loading estimates from the Sacramento and San Joaquin rivers. During 2004, nine years of sediment data were analyzed and sediment loads estimated. The results were written up in a revised sediment section of the “Mallard Island Progress Report” and also submitted to the Journal of Hydrology for review and publication. In addition, we completed a chapter in the progress report on Hg and a further chapter on trace organics loads. These new analyses suggest that our previous estimates for both suspended sediment load and Hg load were high and this has greatly affected the implementation recommendations in the recently released Hg TMDL report (Johnson and Looker, 2003). The question remains as to how accurate are our estimates. The San Francisco Bay is listed (Clean Water Act 303(d)) as impaired for mercury, selenium, PCBs, and chlorinated pesticides. This study aims to address information gaps associated with loadings of these substances (with the exception of selenium) so that a better understanding of relative inputs from urban point and non-point sources, erosion and resuspension in the Bay, and the inputs from the Central Valley rivers can be developed. The RMP TRC endorsed the continuation of the study in future years with the following work plan:
In 2003, the RMP status and trends data from 2001 became available, completing the nine year period employing the original fixed station RMP design. The end of this initial era of the RMP marks an appropriate time to perform a thorough, definitive analysis of the data generated with the original Status and Trends Program design. Nine years of monitoring also represents a substantial body of work for the other aspects of the RMP, and a synthesis of these findings from these elements is also worthwhile at this time. In addition, the last synthetic overview of contamination in the Estuary was completed in 1991 (Davis et al. 1991), and Bay contamination, and understanding and regulation of Bay contamination, have changed considerably since that time.
In 2005, this special study will be completed. The final part of this study is a technical synthesis. In the 2004 workplan this was identified as a technical report: Status and Trends Report – 2001. In discussions in 2004, it was decided to publish this technical synthesis as a special issue of the journal Environmental Research. Dr. Russ Flegal of UC Santa Cruz has agreed to edit the issue and is performing much of the coordination.
These activities will address an objective of the Program that has not yet been adequately addressed: the synthesis of RMP and non-RMP data into an integrated assessment of status and trends in contamination of the Bay and the effective communication of this information. The special issue will effectively communicate RMP information to the scientific community. These articles will also provide a rich resource for development of communication material for nontechnical audiences.
Small tributaries form a major pathway for loads of contaminants that enter the Bay each year. Models developed for the Bay are highly sensitive to the magnitude of loads from small tributaries but present load estimates for this pathway lack accuracy and precision. This study will accurately measure contaminant loads from a small tributary representative of one that may contribute significant loads of sediment and associated contaminants to the Bay, help evaluate the significance of this load as a means of prioritization of further loadings studies, demonstrate a new methodology, and compare these accurate loads measurements to existing simple model estimates.
During WY 2003, the study was funded by the CEP. In WY 2004, the CEP funded the labor portion of the budget ($75k out of $125k). The RMP funded the laboratory analysis portion of the budget ($50k). In WY 2005 USACE has provided $100k for analysis of total, dissolved Hg and total and dissolved MeHg, fieldwork and reporting. SCVURPPP has provided $23k for bed load sampling and Hg analysis, and RMP has provided $50k for trace organics analysis and reporting. The total budget is $173,000, greater then ever before and perhaps an indication of the interest in the study.
The question of incremental contaminant loads to the ecosystem from dredging and in-Bay disposal activities is frequently raised in discussions regarding regulatory policy development (e.g., TMDLs, etc.) suggesting that substantial effects could result. However, to date, the RMP has done little to put numeric bounds on just how much mass of a given contaminant is incorporated into the food web as a result of dredging and in-Bay disposal of dredged sediment. Impairment assessments for the Bay (e.g., mercury, PCBs, dioxins) have focused on accumulation of contaminants in sport fish, and several of the most contaminated fish are benthic foragers that frequent harbors and marinas. The proposed study will build a conceptual model of contaminant transfer to benthic-foraging fish species from dredging activities, including in-Bay disposal, and attempt to identify the steps necessary to give a first-order estimate of the incremental contribution of dredging activities to identified impairments. By focusing on pathways, the proposed work will help refine the box models that have, to now, been the main tool for understanding the fate of contaminants in the Bay. The conceptual model will incorporate the alternative to dredging, which is not dredging, to summarize what is known and needs to be known about availability to the food chain of contaminants associated with sub-surface sediments in depositional areas. The study will synthesize existing knowledge of dredged-sediment quality, suspended sediment dynamics, chemical pathways in bedded sediment, fish distribution, and food-web structures, and will include a review of available literature on these topics.
This project will make recommendations on potential sampling locations in “representative observation watersheds” that could be used to form a “regional network” of contaminant loads monitoring stations. We will synthesize pertinent existing information on contaminant sources and pathways, hydrology, watershed physiography, and land use to prioritize potential representative watersheds for water quality and loads observations. We will then carry out a site reconnaissance in the top six prioritized watersheds to re-rank the watersheds according to on-site logistical constraints. The results will be presented in a technical memo and verbally in a SPLWG meeting
This is a joint project between the Clean Estuary Partnership (CEP) and the RMP to develop a conceptual model and impairment assessment (CM/IA) for polybrominated diphenyl ethers (PBDEs) in the San Francisco Bay. The CEP has allocated $30,000 for SFEI labor to prepare the CM/IA, while the RMP has contributed $25,000 to cover costs of sample analyses to fill in critical data gaps.
The work to be conducted is an impairment assessment and development of a PBDE conceptual model. Given the limited resources and time, this effort will have to be completed by SFEI staff over a 12-month period with oversight from the CEP Technical Committee. The project will include chemical analyses of various field samples to fill critical information gaps, submission of a draft CM/IA report to the CEP Technical Committee for peer-review, and the delivery of a final CM/IA report.
The Air Deposition Pilot Study was suspended after metals and PAH/PCB data were incorporated into the mass budget models. The only remaining component is the measurement of rain samples for mercury to continue as part of the national Mercury Deposition Network through 2004, after which a decision will be made as to whether or not to continue data collection. The project includes SFEI staff time for sampling and trouble-shooting assistance, participation in site audits, and coordination with City of San Jose staff as necessary. The City of San Jose is providing in-kind sampling assistance, with samples being shipped to the MDN laboratory.
In response to the revised RMP objectives and the recommendations of the redesign workgroups, the RMP is developing a new component for the S&T Program to monitor contaminant exposure and effects in the Bay. The RMP is implementing this 5 year Pilot Study to develop several indicators, using resident species, that can provide measures of contaminant exposure and effects at several trophic levels, at different levels of biological organization (biochemical, individual, population, and community levels), and at different spatial scales (locally or regionally).
An Exposure and Effects Workgroup (EEWG) with a 4 member Advisory Panel (Bob Spies, Steve Weisberg, Harry Ohlendorf, and Don Weston) is guiding this Pilot Study. The EEWG has developed a draft five year workplan. The Study is multifaceted, including a variety of different exposure and effects indicators of beneficial use impairment to be tested over the course of five years. Indicators being tested include diving duck muscle (a human exposure indicator), cormorant and Forster’s tern eggs (chemical trend indicators), hatchability of Forster’s terns, least terns, and clapper rails (effects indicators), blood chemistry and biomarkers in harbor seals (exposure and effects indicators), biomarker and effects studies in fish, aquatic and sediment toxicity testing of resident species (effects), and benthic community evaluations using a multimetric approach (effects). Elements to be tested in 2004 are the subject of continuing discussion by the EEWG side-by-side comparison of EPA-laboratory and resident species in dose response studies for aquatic or sediment toxicity tests.
As outlined in the Sources, Pathways, and Loadings Report issued in 2001 (Davis et al. 2001), fairly large uncertainties exist with regard to loading estimates from the two large rivers, and these loads are potentially significant components of the mass budgets for many contaminants. McKee et al. (2002) determined that USGS data on suspended solids concentrations are suitable for estimating suspended solids loads with reasonable confidence, and that these data, if coupled with data on sediment-associated contaminants of concern, could be used to develop estimate contaminant load estimates entering the Bay from the Central Valley in a manner that includes characterization of the large loads that occur during large runoff events. The USGS and other partners currently have funding to continue sampling at Mallard Island until 2004, and at that time, there will be a total of 10 years of nearly continuous data.
In this Special Study (the “Mallard Island Study”), which began in 2002, SFEI is gathering data on sediment-related contaminant concentrations at Mallard Island for the purposes of developing statistical relationships between concentrations and optical backscatter measurements. These relationships can be used to estimate time-continuous concentration data that would then be combined with estimates of discharge to estimate loads. Contaminants being measured include mercury, PCBs, organochlorine pesticides, and PAHs. This work is being performed in collaboration with other groups already carrying out fixed-time and flood-response water sampling (Interagency Ecological Program) so that costs can be reduced and lessons already learned can be readily incorporated into the sampling design. Although this Special Study is closely aligned with the goals of the Clean Estuary Partnership, it also meets the sources and loadings objective of the RMP, and was initiated as part of the RMP.
After ten years of RMP monitoring, it is an appropriate time to perform a retrospective evaluation of the RMP and contamination in the Bay. In 2003, the data from 2001 became available, completing the nine year period employing the original fixed station RMP design. The end of this initial era of the RMP marks an appropriate time to perform a thorough, definitive analysis of the data generated with the original Status and Trends Program design. A decade of monitoring also represents a substantial body of work for the other aspects of the RMP, and a synthesis of these findings from these elements is also worthwhile at this time. In addition, the last synthetic overview of contamination in the Estuary was completed in 1991 (Davis et al. 1991), and Bay contamination, and understanding and regulation of Bay contamination, have changed considerably since that time.
The synthesis of data from the first phase of the RMP will continue to provide a general theme for the Program over the next 2 years. An integrated series of products and events are planned to accomplish an evaluation and long term summary of the many components of the Program. In chronological order, these are:
These activities will address two objectives of the Program that have not yet been adequately addressed, including a rigorous evaluation of long term trends and the synthesis of RMP and non-RMP data into an integrated assessment of status and trends in contamination of the Bay.
The activities that will occur in 2004 are 4, 5, and 6. Workplans and budgets for the developing the Pulse and holding the Annual Meeting are already covered in the 2003 Monitoring Plan under tasks 2.3 (Information Dissemination) and 2.4 (Annual Reporting).
The Sources, Pathways, and Loadings Workgroup (SPLWG) concluded that small tributaries probably represent a significant pathway for contaminant loading to the Bay (Davis et al. 2001). The SPLWG recommended that a study be performed to gather empirical data on small tributary loading. The recommended study was identified as an appropriate project for CEP funding, and the CEP initiated the project in 2003. This project meets the overlapping objectives of both the RMP and CEP.
This Study is applying the same basic technique as in the Mallard Island Study (see 5.1 above), combining continuous monitoring of suspended sediment concentration with strategic collection of samples for chemical analysis. The tributary selected for sampling is the Guadalupe River, which has a major source of mercury in its watershed and suspected sources of PCBs and organochlorine pesticides. The study will accurately measure contaminant loads from a small tributary representative of those that may contribute significant loads to the Bay and demonstrate an innovative method for measuring these loads. Contaminants being measured include mercury, PCBs, organochlorine pesticides and PAHs.
This new special study will evaluate whether information that addresses RMP objectives and management questions can be gleaned from the datasets generated for dredged material testing. For many years dredgers have collected data on the chemical quality and toxicity of Bay sediments from around the fringes of the Bay from a variety of marinas, ports, and waterside marine related businesses, as well as data from the Corps federally maintained navigation channels. This Study will evaluate these data in detail. If the data are found to be valuable to the RMP, a subsequent step would be to establish a data management system for them to make them accessible and usable. The data management system would be included in the 2005 RMP. This effort would meet not only RMP objectives to synthesize information from all sources, but also an objective of the Dredged Material Management Office (DMMO) to make the data publicly accessible. Making these data available would benefit future dredging proponents, the regulatory agencies, interested environmental groups, researchers on overall environmental state of the Estuary, and Estuary habitat restoration entities.
Tasks in this Study will include data compilation, data interpretation, reporting, and development of the beginnings of a data management system. Most of the effort will go to data interpretation and reporting. Data interpretation will include a thorough evaluation of several technical issues with the data, including what data are collected, whether the data are of sufficient quality for rigorous interpretation, and what the samples analyzed are really telling us about the Bay. For example, one question to be answered would be: Is the contamination measured in sediment samples from harbor channels an index of local or regional contamination? While the dredged material testing data may not be directly comparable to RMP data, they may still contain valuable information about contamination and sediment dynamics in the Bay.
This project integrates an existing USGS study by Jim Kuwabara and colleagues with information needs identified by the Clean Estuary Partnership, San Francisco Estuary Institute, San Francisco Regional Water Resources Control Board and local stakeholders. Specifically, it will provide initial determinations of dissolved total and methyl-mercury flux from the sediments into the water column of South Bay. These determinations will be made at two times in the year: once following the spring phytoplankton bloom in the South Bay, and the other during late summer when, in contrast, surficial settling of biogenic material would be minimal. The time-series of concentration data will be used for flux calculations that directly include bioturbation effects.
Quantifying and understanding the magnitude and variability of these fluxes are critical to the accurate assessment of sources and loads of biologically reactive forms of contaminants as well as to the development of process-integrated water-quality models for this Estuary. A progress report on the 2003 sampling will be provided in summer 2004. The final report on this effort will be provided to SFEI by June 2005.

Unlike the static Status and Trends program, the purpose of the pilot and special studies element is to provide a means to react quickly to emerging issues of concern or to evaluate new methods that may later be incorporated into Status and Trends. It allows the program to be flexible to adapt to new information or conversely new information needs.
In brief, the procedure includes the following steps:
The purpose of the study selection process is to
RMP Projects include Status and Trends projects, which recur annually or every few years, and Pilot and Special Studies, which are funded for a specific time period.
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RMP data can be accessed via our Web Query Tool. Results provided are updated as needed with reanalyzed results and corrections. The database was last updated on 5/18/10. Contact Cristina Grosso for recent changes.
One of the main principles of the RMP is to obtain and provide data in a timely manner to a variety of potential users. All RMP data goes through both an internal and external review before it is released to the public. The purpose of this Policy Statement is to provide some guidelines for usage, reporting, and publication of RMP data. It is not the intent of this Policy to restrict RMP data usage or availability.
All of the RMP data have been obtained and analyzed using funding from Bay dischargers and dredgers. Therefore, the data are public domain and the RMP cannot constrain the availability or usage of the data. However, prudent usage, knowledge of the data quality, and professional courtesy should all be considered in obtaining and using RMP data.
The first obligation of RMP investigators and participants is to provide RMP data to SFEI to assure publication in a timely manner. RMP publications include written contributions from lead investigators, collaborating scientists, and SFEI staff. Pilot and Special Studies summaries will usually be written under contract by the lead investigator. Upon recommendation by the Technical Review Committee, the Steering Committee will determine the content of the RMP publications.
The results provided by the web query tool may differ from those previously reported in the RMP publications and static data tables, due in part to ongoing updates to the dataset, standardization of the qualifiers reported, changes in the handling of replicate samples, and changes in the method used to sum the dissolved and particulate water fractions.
This study performs monthly water sampling in 2010 to map the spatial distributions of basic water quality parameters along the entire Bay-Delta system. Measurements will include salinity, temperature and dissolved oxygen, which influence the chemical form and solubility of some trace contaminants; suspended sediments and phytoplankton biomass, which influence the partitioning of reactive contaminants between dissolved and particulate forms. This basic information is required to follow the seasonal changes in water quality and estuarine habitat as they influence biological communities and the distribution and reactivity of trace contaminants.
Highlights from this work were described by Dr. Cloern at the 2009 Annual Meeting as well as an article in the 2006 Pulse of the Estuary.
An online database is provided by USGS, allowing users to look at the water quality data collected from 1969 until present.
Jim Cloern, USGS Menlo Park, California
There have been numerous changes over the years to the RMP in order to better address management questions and adapt to changing regulatory and scientific information needs. Changes have been made to the sampling design, target analyte list, stations sampled, laboratories performing the analyses, and laboratory methods. The summary also indicates when data have been rejected or are not available through the Web Query Tool.
To view a summary of Changes to the RMP as a PDF file please click here.
CD3 enables users to perform spatial queries of water quality data from the San Francisco Estuary and Delta. Data can be dynamically mapped and downloaded as an Excel file. New datasets are regularly made available through this tool.
Two versions of this tool are available. A stand-alone version exists for Internet Explorer. Non-Internet Explorer browsers are able to use the tool with some added features. Users will automatically be forwarded to the appropriate version.
Data from the following programs are available through CD3. Click here for more detailed information on the datasets.
All data have gone through extensive QA/QC and only data that have successfully passed the QA process are provided. However, CD3 does not provide access to QA/QC data at this time.
For more information regarding the type of data made available through CD3, as well as how to interpret downloaded results, please consult the Data Handling page.
2009 improvements included:
The RMP Target Analyte List provides current target analytes and their reporting units. The list is broken up into several tables. Page 1 has Field Measures taken during sampling. Pages 2 and 3 list conventional quality and trace element analytes. Pages 4 through 7 discuss trace organic analytes. Page 8 lists Special Study analytes.
To view the RMP Target Analyte List as a PDF file please click here.
The Reportable Analyte Tables (available in PDF form below) summarize analytes available via the Web Query Tool. Shaded areas indicate analytes that are available for that year. Results are not available when data are determined to be not reportable, when sampling for a particular analyte has ended, or when the sampling plan includes analysis of an analyte on a variable schedule.
Analyte Type Code Key:
Click here for the Reportable Analytes for Water.
Click here for the Reportable Analytes for Sediment.
Click here for the Reportable Analytes for Bivalve Tissue.
Please note that beginning in 2007, bivalve monitoring occurs biennially for trace organics and every five years for trace metal analytes. In addition, bivalves were not deployed in 2007.
Area weights are used in the generation of the cumulative distribution function (CDF) plots and the summary statistics. The total area sampled in the five Estuary regions is adjusted for regional area weights using the spsurvey package which is available for the R software environment for statistical computing and graphics. The CDF plots and summary statistics for the individual regions are not adjusted.
In the initial sampling design, area weights were calculated for 100 water and 140 sediment sites per region. Each region’s original sample frame area is shown in the table below. No random samples were allocated to the Rivers region; therefore, that region was not included in the total sample frame.
| Region Code | Region Name | Area of Sample Frame for Sediment (km²) |
Area of Sample Frame for Water (km²) |
|---|---|---|---|
| RIV | Rivers | 0 | 0 |
| SU | Suisun Bay | 80.357 | 72 |
| SPB | San Pablo Bay | 226.821 | 181 |
| CB | Central Bay | 396.442 | 382 |
| SB | South Bay | 185.171 | 144 |
| LSB | Lower South Bay | 7.642 | 5 |
| Totals: | 896.433 | 784 |
The area weights, however, must be re-calculated each year according to the actual number of sites sampled; by dividing the product of the total sample frame area used for sample selection and the original area weights, by the sum of the original weights for the targeted sites. The targeted sites include sites that could not be sampled for any reason (as one needs to adjust for the area that could not be sampled; for example any site that was not accessible during the sampling cruise), and replacement sites. Therefore, the area weight assigned to each sample will decrease, and the power of analysis will increase as the spatial coverage of the Estuary increases and more samples are collected over time. The re-calculated area weights for each region for the period 2002-2010 are shown in this excel file.
For more information, please contact John Ross at johnr@sfei.org
This page describes how statistics on contaminant concentrations in San Francisco Bay sediments are compiled and updated for use in the dredged material testing program.
RMP sediment data collected since 2002 form the basis for calculating both the Dredged Material Management Office (DMMO) bioaccumulation testing trigger concentrations (BTs) for mercury, PCBs and PAHs, and the TMDL-based in-Bay disposal limits for mercury and PCBs. The BTs are calculated using the 90% Upper Tolerance Limit (UTL) of the 90th percentile concentrations of mercury, PCBs, and PAHs, while the TMDL-based limits for mercury and PCBs are calculated using the 90% Upper Tolerance Limit of the 99th percentile concentrations. These values are intended to be based on the most recent 10 years of RMP sediment data. However, prior to 2002, the RMP sampling design consisted of repeated sampling of fixed stations along the spine of the Estuary. In 2002 the RMP adopted a probabilistic (random, spatially balanced) sampling design to obtain a more representative characterization of conditions throughout the Bay, and only the newer data are used in calculating the BTs and TMDL-based limits. Therefore the 2011 BTs and TMDL-based limits were based on only eight years of data (2002-2009), while the BTs and TMDL-based limits for 2012 are based on nine years of data (2002-2010). Starting in 2013, the BTs and TMDL-based limits will be recalculated using the most recent 10 years of data. Since the newest 10-year data set is used to calculate each year's thresholds, the individual values are expected to change slightly each year and may be higher or lower than the previous year.
The DMMO will make suitability determinations for in-Bay disposal using the BT and TMDL thresholds in effect at the time of the determination. In general, BT and TMDL thresholds in effect at the time a suitability determination is made will remain valid as long as the suitability determination holds: for example, even if the material is not dredged until a subsequent year or if the determination includes a Tier I testing exclusion for a future dredging episode. However, if conditions have changed substantially enough for the DMMO to require a new round of testing and a new suitability determination, the thresholds in effect at the time of the new suitability determination will be used.
The summary table below presents the calendar year 2012 BTs for mercury, PCBs, and PAHs and the calendar year 2012 TMDL-based in-Bay disposal limits for mercury and PCBs, after removal of any statistical outliers. Further details on the calculation of these thresholds are provided in the links below. Note: the actual BTs used by DMMO agencies are based on the 90th UTL of the 90th percentile concentrations shown, but rounded to the nearest two significant figures. Thresholds for prior years are also shown.
For questions, contact Beth Christian (echristian at waterboards.ca.gov; 510-622-2335).
| Contaminant | 90% UTL of 90th percentile |
DMMO BTs | 90% UTL of 99th percentile (TMDL Disposal Limits) |
Notes |
| Hg (mg/kg dry wt.) | 0.341 | 0.34 | 0.471 | Total Mercury |
| PCB (μg/kg dry wt.) | 16.8 | 17 | 26.41 | Sum of 40 congeners2 |
| PAH (μg/kg dry wt.) | 4,735 | 4,700 | Sum of 25 PAHs2 |
| Contaminant | 90% UTL of 90th percentile |
DMMO BTs | 90% UTL of 99th percentile (TMDL Disposal Limits) |
Notes |
| Hg (mg/kg dry wt.) | 0.334 | 0.33 | 0.472 | Total Mercury |
| PCB (μg/kg dry wt.) | 15.7 | 16 | 19.5 | Sum of 40 congeners2 |
| PAH (μg/kg dry wt.) | 4,847 | 4,800 | Sum of 25 PAHs2 |
1The difference in the PCB TMDL limit from 2011 to 2012 resulted largely from three PCB values that were identified statistically as outliers in the 2002-2009 data set, but that are no longer statistical outliers in the 2002-2010 data set. Specifically, some of the data collected in 2010 filled in gaps at the higher end of the PCB distribution, causing the former outlier data to now be included in the calculations (histogram of 2002-2010 PCB values).
2The RMP reports total PCBs and PAHs using slightly different analyte lists and/or analytical methods than those shown in the DMMO's “Guidelines for Implementing the Inland Testing Manual in the San Francisco Bay Region”. For PCBs, instead of the Aroclor mixtures, the RMP reports a sum of 40 PCB congeners. For dredged material testing, the DMMO recommends USEPA Method 8082 which employs gas chromatography/electron-capture detection (GC/ECD) capable of achieving per congener detection limits in the 0.1 – 0.6 μg/kg range and reporting limits in the 0.5 – 1.0 μg/kg range. Alternative analytical methods may be acceptable as long as the detection and reporting limits are comparable to those of Method 8082. For PAHs, the RMP reports a slightly expanded list of PAH compounds (25 compounds vs. the previous DMMO list of 16). Since all the PAHs in this expanded list are measured by the same analytical method most commercial laboratories already use when analyzing sediment samples (EPA 8270 SIM), there should be little or no cost increase for reporting the additional PAHs.
In order to make direct comparisons of dredging project sediment chemistry results to BTs and TMDL limits, it is important that dredgers report total PCBs and total PAHs in the same manner as the RMP. The target analytes are shown in this table.
As part of the copper site-specific objective, NPDES dischargers are required to calculate annually the three-year rolling average of dissolved copper concentrations in water in each segment of the Bay, based on RMP data. This table presents the segment average and corresponding trigger levels in the Basin Plan. The average includes data from randomized as well as historical sites in the segments, although it excludes data from the historical reference site outside the Golden Gate.
| Bay Segment | Trigger (μg/L) | 2008-2010 Rolling Average (μg/L) | Number of Samples Included in Average | Notes |
| Lower South Bay | 4.2 | 3.44 | 15 | |
| South Bay | 3.6 | 2.81 | 12 | Historical Station BA30 included |
| Central Bay | 2.2 | 1.36 | 12 | Historical Station BC10 included |
| San Pablo Bay | 3 | 1.73 | 9 | |
| Suisun Bay | 2.8 | 2.16 | 9 |
The RMP produces annual reports and newsletters to update managers, stakeholders, and other interested parties. The Annual Monitoring Results is a summary of the year's sampling events, analysis, and Pilot and Special Studies. The Pulse of the Estuary highlights major findings of each year's activities and synthesizes the data with other regional findings.
The purpose of The Pulse is to make the most important information available on water quality in the San Francisco Estuary accessible to water quality managers, decision-makers, scientists, and the public.
2010 |
2009 |
2008 |
2007 |
2006 |
2005 |
2004 |
2003 |
2000 |
1999 |
1998 |
For a hard copy of the Pulse, please send your name, address, and the quantity to linda@sfei.org
For comments, corrections and content and photo updates, please contact Jay Davis at jay@sfei.org
The San Francisco Estuary Institute has been collecting water, sediment and tissue samples from the San Francisco Bay and tributaries since 1993. These samples are analyzed for ancillary parameters, trace metals and trace organics. Each year a summary of the year's sampling events is published in the Regional Monitoring Program’s Annual Monitoring Results. The results and associated graphics can be accessed using the Web Query Tool.
2009 Annual Monitoring ResultsFull Report (2 MB PDF) |
2008 Annual Monitoring ResultsFull Report (3 MB PDF) |
|
2007 Annual Monitoring ResultsFull Report (3 MB PDF) |
2006 Annual Monitoring ResultsFull Report (19 MB PDF) |
|
2004-2005 Annual Monitoring ResultsFull Report (17.5 MB PDF) |
|
Every 3 years, the RMP publishes a report intended for the general public summarizing the results of the most recent sport fish monitoring, which began in 1997 and occurs on a triennial basis.
Contaminants in Sport Fish from the California Coast, 2009: Summary Report on Year One of a Two-Year Screening Survey |
Contaminant Concentrations in Sport Fish from San Francisco Bay 2006 |
Contamination Concentrations in Fish from San Francisco Bay, 2003 |
Contaminant Concentrations in Fish from San Francisco Bay, 2000 |
Contamination Concentrations in Fish from San Francisco Bay 1997 |
The RMP is developing a series of fact sheets on contaminants of emerging concern (CECs). The fact sheets are intended to serve as a quick reference for media, regulators, decision-makers, and scientists to allow communication of accurate information to the public. Each fact sheet will summarize our current understanding of a select CEC, including the latest data and concerns for San Francisco Bay.
Alkylphenol Ethoxylates
Carbamazepine
Spring/Summer 2008, Volume 13, Issue 1
The RMP hosts two conferences each year, focusing on on-going science in the estuary. The RMP Annual Meeting, held in early fall, unites RMP stakeholders to discuss current RMP projects and highlight one area of research, such as stormwater, sediment, mercury, or emerging contaminants. The Annual Mercury Meeting, held in the beginning of each year, brings together scientists and policy makers to review the state of mercury and methylmercury research and discuss how it should inform environmental policy. The RMP also hosts an annual Quality Assurance/ Quality Control workshop to bring together field researchers and labs, in an effort to improve the QA/QC process.
Ag: The chemical symbol for silver, a trace metal measured by the RMP.
Al: The chemical symbol for aluminum, a trace metal measured by the RMP.
aliquot: A subsample taken from a field sample (e.g., of sediment).
ambient: Refers to the overall conditions surrounding a place or thing. In the case of the RMP, ambient monitoring is used to determine existing pollutant levels in the San Francisco Estuary.
ammonia: A colorless gas which is less dense than air and has a penetrating odor. It is the fourth largest industrial chemical produced, with over 80% used in the manufacturing of agricultural fertilizers.
amphipods: An order of small shrimp-like crustaceans, such as sand fleas. Many live on the bottom of the Estuary (i.e., are benthic) and feed on algae and detritus.
analyte: A targeted compound that is analyzed in a test.
anthropogenic: Effects or processes that are derived from human activities, as opposed to natural effects or processes that occur in the environment without human influences.
arenaceous: Resembling, derived from, or containing sand.
arthropod: Any member of a large phylum of invertebrate animals with jointed legs and a segmented body, such as insects, crustaceans, arachnids, myriapods, and trilobites.
As: The chemical symbol for arsenic, a trace element measured by the RMP.
assemblage: A group of persons, animals, plants, or things gathered together.
(automated) Winkler titration: The process of determining the amount of a certain substance contained in a known volume of a solution by measuring volumetrically how much of a standard solution is required to produce a given reaction.
axial transect: A line which follows the deep channel along the length or "axis" of the Estuary. Most RMP stations are on this axial transect, also known as the "spine".
Base Program: Standard RMP monitoring conducted primarily for the purposes of characterization and trends, i.e. water, sediment, and tissue cruise sampling and analyses at the stations normally sampled, excluding special and pilot studies.
Basin Plan: The SFBRWQCB's plan for the Estuary basin. This includes the land and waters within the boundaries of the immediate San Francisco Bay watershed, Suisun Marsh, and the western part of the Sacramento-San Joaquin Delta.
benthos, benthic Bottom dwelling; non-planktonic; attached to or resting on the substrate.
bioaccumulation: The buildup of contaminants in an organism's tissues (usually fatty tissue) through ingestion, or contact with the skin or respiratory tissue. Contaminants that bioaccumulate may also biomagnify in the food web, resulting in higher tissue concentrations in predators relative to ambient environmental concentrations.
bioassay: A laboratory test using live organisms to measure biological effects of a substance, factor, or condition. The effect measured may be growth, reproduction, or survival.
bioavailability: The extent to which a compound is available for intake by organisms. Bioavailable compounds have the potential to cause biological effects, such as increased mortality.
biogeochemical cycle: The cycle in which nitrogen, carbon, and other inorganic elements of the soil, atmosphere, etc. of a region are converted into the organic substances of animals and plants of the region and released back into the environment.
biological condition index: A measure of the biological condition of RMP transplanted bivalves expressed as the ratio of tissue dry weight to shell cavity volume.
biomagnification: The net effect of bioconcentration (accumulation of pollutants via dermal or respiratory tissue exposure), bioaccumulation (accumulation via ingestion), and depuration (excretion or loss of pollutants via metabolic processes).
biomass: Total weight of all organisms in a particular habitat or area.
biomonitoring: Monitoring conducted to determine existing environmental conditions, pollutant levels, rates, or species in the environment.
biota: The animals, plants, and microbes that live in a particular location or region.
bivalves: Any mollusk, such as an oyster or clam, that has a shell with two hinged "valves" or shell halves.
blooms (algal): A population burst that remains within a defined part of the water column.
brackish: Somewhat salty water that is less salty than seawater.
calcareous: Being made of calcium carbonate.
Cd: The chemical symbol for cadmium, a trace metal measured by the RMP.
chironomids: Small, two-winged flies in the adult stage, closely related to mosquitoes and Chaoborus (Phantom Midge or Glassworm). Most lay eggs singularly or in strings while skimming over the water surface. The eggs hatch into larvae and form mud tubes from bottom material and muscous. A few species have free swimming larva.
chlordanes: A contact insecticide used in agriculture until 1978 to control soil pests, particularly termites. It belongs to a group of closely related organochlorines, which includes aldrin, dieldrin, endosulfan, and heptachlor.
chlorinated hydrocarbons: A group of organic compounds which includes PCBs, DDTs, chlordanes, and dieldrin.
chlorophyll a: A key substance in the process of photosynthesis. It is found with photosynthesizing organisms and is used in the RMP as a measure of the abundance of photosynthetic organisms in the water column (phytoplankton).
community: The organisms inhabiting a common environment and interacting with one another.
congener: A compound of the same kind.
conventional pollutant: As specified under the federal Clean Water Act, conventional pollutants are total suspended solids, fecal coliform bacteria, biochemical oxygen demand, pH, oil, and grease. In addition, there are a large number of nonconventional and toxic pollutants that are of concern.
copepod: A type of herbivorous microscopic crustacean. They are important in the food chain because they are eaten by many fish or by other organisms that are eventually eaten by fish.
Cr: The chemical symbol for chromium, a trace metal measured by the RMP.
criterion: A standard rule or test on which a judgment or decision can be based.
crustacean: Any of a class of arthropods, including shrimps, crabs, barnacles, and lobsters, that usually live in the water and breathe through gills; they have a hard outer shell and jointed appendages.
Cu: The chemical symbol for copper, a trace metal measured by the RMP.
DDD (dichlorodiphenyldichlorethane): DDD was a commonly used pesticide in the past, but is now banned in the United States.
DDE (dichlorodiphenyldichloroethylene): DDE is found in the environment as a result of the breakdown of the insecticide DDT. DDE has been listed as a pollutant of concern to the U.S. EPA's Great Waters Program due to its persistence in the environment, potential to bioaccumulate, and toxicity to humans and the environment. See also DDTs.
DDT (dichlorodiphenyltrichloroethane): The combination of DDT and its degradation products, DDD and DDE. A chlorinated hydrocarbon that was a highly effective, but extremely persistent organic pesticide. DDT was extensively used in the past for the control of insects (crop protection and disease control). In 1972 its use was banned in the United States, except in the case of a public health emergency.
Delta Outflow Index (DOI): Freshwater flows from the Delta into San Francisco Bay. The DOI is calculated as total Delta inflow plus precipitation, minus in-Delta uses and exports.
depuration: The loss of contaminants from an animal's gut or tissue.
"detectable difference" criterion: A significance test which is based on the minimum significant difference (MSD) values.
dinoflagellate: Any of numerous minute, chiefly marine protozoans or algae of the order Dinoflagellata, having two flagella and a cellose-covering. They are a main constituent of plankton.
dischargers: Public and private organizations that discharge treated wastewater, cooling water, or urban runoff, or are involved in dredging activities.
dissolved compounds: Compounds that are present (dissolved) in the water and, therefore, are available for fish and other aquatic animals.
dry-season sampling period: RMP sampling carried out between July and September.
Effects Range-Low (ERL): Part of the Effects Range sediment quality guidelines, established by the National Oceanic and Atmospheric Administration. The guidelines were developed to identify concentrations of contaminants associated with biological effects in laboratory, field, or modeling studies. The ERL value is the concentration equivalent to the lower 10th percentile of the compiled study data. Sediment concentrations below the ERL are interpreted as being "rarely" associated with adverse effects. See also ERM.
Effects Range-Median (ERM): Part of the Effects Range sediment quality guidelines established by the National Oceanic and Atmospheric Administration. The guidelines were developed to identify concentrations of contaminants associated with biological effects in laboratory, field, or modeling studies. The ERM is the concentration equivalent to the 50th percentile of the compiled study data. Sediment concentrations above the ERM are "frequently" associated with adverse effects. See also ERL.
effluent: An outflow from a sewer or sewage system.
ELISA analysis: Enzyme-linked immunosorbent assay that tries to determine the nature, proportions, and function of the examined parts.
El Niño: El Niño is a disruption of the ocean-atmosphere system in the tropical Pacific and have important consequences for weather around the globe.
elutriate: To purify, separate, or remove by washing, decanting, and settling.
embayment: Forming into a bay or a formation resembling a bay.
equilibrium predictions: A theoretical model or experimental determination of reactions, that describes the ratio of concentrations of the product to the reactant. It expresses chemical activity in terms of related concentration.
estuary: A body of water at the lower end of a river which is connected to the ocean and semi-enclosed by land. In an estuary, sea water is measurably diluted by freshwater from the land.
Fe: The chemical symbol for iron, a trace metal measured by the RMP.
fluorometer: An instrument to detect and measure the emission of fluorescence.
food web: The rather linear food chains (from plants through herbivores and carnivores) tend to be woven into a complex food web, where energy is transferred to all different levels.
foraminifera: Protozoan group (usually) secreting a calcareous shell; both planktonic and benthic representatives exist.
genus: A classification of plants or animals with common distinguishable characteristics. It is the main subdivision of a family and is made up of a small group of closely related species or of a single species.
grab: Benthic sampling device with two or more curved metal plates designed to converge when the sampler hits the bottom and grab a specific volume of sediment.
gravimetric method: Measurements by weight or of the pull of gravity.
guidelines: Comparisons to guidelines were made to provide a context for evaluating the condition of the Estuary in terms of contamination, and not for any regulatory purpose. Guidelines were selected based on guidance from the San Francisco Bay Regional Water Quality Control Board.
HCH (hexachlorocyclohexane): A manufactured chemical that exists in eight forms, or isomers.
Hg: The chemical symbol for mercury, a trace metal measured by the RMP.
hydrocarbons: Organic compounds containing carbon and hydrogen.
none
none
none
ligand: An ion, a molecule, or a molecular group that binds to another chemical entity to form a larger complex.
linear regressions: A common practice in science to try to explain natural phenomena by models. The true regression of Y on X consisting of the means of populations of Y values, where a population is determined by X values. The regression line needs to be straight to develop a computation procedure.
LC50: The concentration of a contaminant that is lethal to half the organisms in a bioassay.
loadings: The total amount of material entering a system from all sources.
marshes: A wetland where the dominant vegetation is non-woody plants, such as grasses and sedges, as opposed to a swamp where the dominant vegetation is woody plants, such as trees.
matrix: Any non-living, intercellular substance, in which living cells are embedded, as in bone, cartilage, etc.
mean Effects Range-Median quotient: Reflects the increasing contaminant concentrations in sediment from many contaminants and appears to provide a useful way to express the degree of overall sediment contamination. It was shown to have a highly significant correlation with amphipod survival.
method detection limit (MDL): The minimum concentration of a substance that can be measured and reported with 99% confidence that the analyte concentration is greater than zero. It is determined by analysis of a sample in a given matrix containing the analyte.
microfauna: Animals whose shortest dimension is less than 0.1 mm.
minimum significant difference (MSD): The lowest distinguishable difference that is statistically meaningful.
morphology: The study of form and structure, at any level or organization.
mysid: Small, shrimp-like, chiefly marine crustaceans of the order Mysidacea.
National Pollutant Discharge Elimination System (NPDES): A provision of the Clean Water Act that prohibits discharge of pollutants into waters of the United States unless a special permit is issued by the U.S. EPA, a state, or other delegated agency.
neap tide: Tides with the smallest height difference between high tide and low tide, usually occurring during the moon's quarters. Compare with spring tide.
nematode: Any of a phylum of worms, often parasites of animals and plants, with long, cylindrical, unsegmented bodies and a heavy cuticle (e.g., hookworm, pinworm).
Ni: The chemical symbol for nickel, a trace metal measured by the RMP.
Niskin bottle: An oceanographic water sampling device.
oligochaete: Any of a class of segmented worms, such as the earthworm, lacking a definite head and having relatively few body bristles. They are mostly found in moist soil and freshwater.
oligotrophic: Water bodies or habitats with low concentrations of nutrients.
optical backscatter sensor: An instrument that measures total suspended solids (TSS), organic and inorganic particles of all sizes, in a certain volume of water.
organochlorine: A group of organic chemicals to which varying amounts of chlorine have been added. Organochlorine or chlorinated hydrocarbons (insecticides) are part of a broader class of halogenated hydrocarbons.
oxygen electrode: A terminal that conducts an electric current into or away from various conducting substances and collects and controls the flow of oxygen electrons.
"p" value: A confidence coefficent or a statistical value used in the multiple comparison procedure for comparing several treatments with a control.
PAHs (Polycyclic or Polynuclear Aromatic Hydrocarbons): A class of complex organic compounds, some of which are persistent and carcinogenic. PAHs are formed from the combustion of organic material and are ubiquitous in the environment.
particulate: A small, solid piece of matter that is easily lifted into the air, such as dust or ash. Smaller, fine particulates are more hazardous than larger, coarse ones because they are more easily inhaled deep into the lungs.
Pb: The chemical symbol for lead, a trace metal measured by the RMP.
PCBs (Polychlorinated Biphenyls): A group of manufactured chemicals including 209 different, but closely related, compounds made up of carbon, hydrogen, and chlorine. If released to the environment, they persist for long periods of time and can biomagnify in the food web. They are an organic toxicant suspected of causing cancer, endocrine disruption, and other adverse impacts on organisms.
pH: The acidity of water. A water quality parameter analyzed by the RMP.
peristaltic: Rhythmic, wavelike motion of the walls of the alimentary canal and certain other hollow organs. Alternating contraction and dilation of transverse and longitudinal muscles move the contents of the tube through the system.
pesticide: A general term to describe chemical substances used to destroy or control pest organisms, including herbicides, insecticides, algicides, and fungicides.
phaeophytin: A gray accessory plant pigment in green leaves. Accessory pigments help the plant to make more efficient use of sunlight because, unlike chlorophyll, they can trap energy from the wavelengths of light.
phytoplankton: Microscopic photosynthesizing organisms that drift with the currents.
pilot study: A study which employs methods that are under evaluation for potential incorporation into the RMP.
pollutant: A substance that adversely alters the physical, chemical, or biological properties of the environment.
pollution-index species: Species that are sensitive to a certain pollutant and that are monitored in terms of abundance and death in unpolluted and polluted areas. Measured in deaths per unit of pollution.
polychaete: ("with much hair") Any of a class of primarily marine, annelid worms that have a pair of fleshy, leg-like appendages covered with bristles on most segments.
principal components analyses (PCA): A method that gives ecologists their first ordination technique in which ordination scores are derived from the data matrix alone. It involves the simultaneous production of species and sample ordination scores in one integrated analysis. PCAs are used for the indication and indirect measurement of environmental complexes.
protozoan: Any of a large group of single-celled, usually microscopic eukaryotic organisms, such as amoebas.
pseudopod: A temporary cytoplasmic protrusion from an ameobid cell which functions in locomotion or in feeding by phagocytosis.
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red tide: A dense outburst of phytoplankton (usually dinoflagellates) often coloring the water reddish brown.
resuspension: The condition of a substance whose particles are dispersed through a fluid but not dissolved in it.
runoff: An overflow of fluid not absorbed by soil, such as rainfall.
salinity: The number of grams of dissolved salts in 1,000 grams of sea water. In the RMP it is expressed as (parts per thousand).
screening value (SV): tissue screening values (SVs) for use in State fish/shellfish consumption advisory programs for the general adult population* from table 5-2 of EPA document #823-R-95-007 (Methods for Sampling and Analyzing Contaminants in Fish and Shellfish Tissue)
Se: The chemical symbol for selenium, a trace element measured by the RMP
sediment pore water: The parts of water that are in channels or passages in the suspended material on the bottom of a fluid through which it may be absorbed or discharged.
sediment quality guidelines (SQG): The National Oceanic and Atmospheric Administration (NOAA) provided these guidelines, which are based on data compiled from numerous studies in the United States that linked sediment contamination and biological effects information. They were developed to identify concentrations of contaminants associated with biological effects in laboratory, field, or modeling studies
sediment quality triad: A sediment assessment technique that incorporates information about sediment chemistry, toxicity, and benthos. The RMP is monitoring all three components and uses this information to evaluate the condition of the estuarine sediment.
sediment water interface (SWI): An exposure system that mimics situations that may occur in nature when negatively buoyant bivalve embryos contact sediment before hatching. Comparison of test results with other manipulating tests allows for the evaluation of possible effects related to the elutriate preparation process.
semidiurnal tide cycle: The two high and two low tides per lunar day (24.84 hours). In the San Francisco Bay-Delta, the cycle is known as a mixed semidiurnal cycle, since the two high and the two low tides are of unequal height.
shoals (broad and lateral): Shallows or sandbars in a body of water.
special study: A study initiated by the RMP in order to help improve interpretation or collection of RMP data.
speciation: The process of formation of a new species.
species:A fundamental biological classification, comprising a subdivision of a genus and consisting of a number of plants or animals all of which have a high degree of similarity, can generally interbreed only among themselves, and show persistent differences from members of allied species.
spectrophotometric method: A method used for comparing the color intensities of different spectra.
spring tide: Tides with the greatest range between highs and lows, usually occurring during the full or new moons. Compare with neap tide.
sulfides: A compound of sulfur with another element or a radical.
suspended-solids concentration (SSC): Organic or inorganic particles that are suspended in and carried by water. The term includes sand, mud, and clay particles, as well as solids in wastewater.
taxon: A group of organisms that has been formally named (e.g., species, genus, family, order, etc.).
tolerance limits: It is the maximum amount of a contaminant residue legally permitted by U.S. EPA, for example in drinking water.
total maximum daily load (TMDL): The TMDL process provides a flexible assessment and planning framework for identifying load reductions or other actions needed to attain water quality standards (i.e., water quality goals to protect aquatic life, drinking water, and other water uses). The Clean Water Act §303(d) established the TMDL process to guide application of state standards to individual water bodies and watersheds.
total organic carbon (TOC): This is the sum of organic carbon and is a monitoring parameter analyzed in environmental water programs. It is a physical sediment factor which can influence the concentration of other compounds. Represented variations in concentration can be attributable to spatial and temporal variations in sediment type.
toxic: Poisonous, carcinogenic, mutagenic, teratogenic, or otherwise directly harmful to life.
toxic equivalent: The combined potency of complex mixtures of compounds as an equivalent in toxicity.
toxic hot spots: Locations in enclosed bays, estuaries, or the ocean where pollutants have accumulated in the water or sediment to levels which (1) may pose a hazard to aquatic life, wildlife, fisheries, or human health, (2) may impact beneficial uses, or (3) exceed State Water Resources Control Board or Regional Water Quality Control Board-adopted water quality or sediment quality objectives.
toxicity: A measure of characteristics which are poisonous, carcinogenic, or otherwise harmful to life.
toxicity identification evaluation (TIE): A process used to determine the compound(s) responsible for toxicity in ambient waters, effluents, and sediments.
trace contaminants: Substances that pollute another substance, air, or water, and are found in low concentrations.
trace element: One of a group of naturally occurring elements found in low ("trace") concentrations in the water, sediment, and tissue measured by the RMP.
trace organic: An organic compound found in low ("trace") concentrations in the water, sediment, and tissue measured by the RMP.
transport: To carry from one place to another, especially over long distances.
trophic level: Representing one step in the food web with number of individuals, energy, or biomass.
trophic transfer: The energy transfer from one trophic level to another.
Total Suspended Solids (TSS): Organic and inorganic particles of all sizes suspended in a measured volume of water.
t-test: Statistical method for testing differences between two samples.
upstream: In the direction against the current of a stream.
upwelling: Vertical or upward movement of water. This usually occurs near the coasts and is driven by onshore winds that bring nutrients from the depths of the ocean to the surface layer.
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water column: The water in a lake, estuary, or ocean which extends from the bottom sediments to the water surface. The water column contains dissolved and particulate matter and is the habitat for fish, plankton, and marine mammals.
water quality criteria: Specific levels of water quality which, if exceeded, are expected to render a body of water unsuitable for its designated beneficial use.
water quality guidelines: Specific levels of water quality which, if reached, may adversely affect human health or aquatic life. These are non-enforceable guidelines issued by a governmental agency or other institution.
wet-season sampling period: RMP sampling carried out between January and April.
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Zn: The chemical symbol for zinc, a trace metal measured by the RMP.