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Marine Exotic Species in the Caribbean: A Progress Report. University of Puerto Rico/Isla Magueyes Laboratory, La Parguera, Puerto Rico.2002.
A Mass Budget of Polybrominated Diphenyl Ethers in San Francisco Bay, CA. Environment International.2008.
Measurement of sediment and contaminant loads from the Guadalupe River watershed: sampling and analysis plan. SFEI Contribution No. 64. San Francisco Estuary Institute: Oakland, CA.2002.
Mechanical shredding of water hyacinth (Eichhornia crassipes): mpacts to water quality in the Sacramento-San Joaquin River Delta, California. Estuaries 30, 627-640 . SFEI Contribution No. 525.2007.
A Menu of Fire Response Water Quality Monitoring Options and Recommendations for Water Year 2019 and Beyond. SFEI Contribution No. 889. San Francisco Estuary Institute : Richmond, CA.2018.
Mercury and Methylmercury in Fish and Water from the Sacramento-San Joaquin Delta: August 2016 – April 2017. SFEI Contribution No. 908. Aquatic Science Center: Richmond, CA.2018.
Monitoring of sport fish and water was conducted by the Delta Regional Monitoring Program (Delta RMP) from August 2016 to April 2017 to begin to address the highest priority information needs related to implementation of the Sacramento–San Joaquin Delta Estuary Total Maximum Daily Load (TMDL) for Methylmercury (Wood et al. 2010). Two species of sport fish, largemouth bass (Micropterus salmoides) and spotted bass (Micropterus punctulatus), were collected at six sampling locations in August and September 2016. The length-adjusted (350 mm) mean methylmercury (measured as total mercury, which is a routinely used proxy for methylmercury in predator fish) concentration in bass ranged from 0.15 mg/kg or parts per million (ppm) wet weight at Little Potato Slough to 0.61 ppm at the Sacramento River at Freeport. Water samples were collected on four occasions from August 2016 through April 2017. Concentrations of methylmercury in unfiltered water ranged from 0.021 to 0.22 ng/L or parts per trillion. Concentrations of total mercury in unfiltered water ranged from 0.91 to 13 ng/L.
Over 99% of the lab results for this project met the requirements of the Delta RMP Quality Assurance Program Plan, and all data were reportable. This data report presents the methods and results for the first year of monitoring. Historic data from the same or nearby monitoring stations from 1998 to 2011 are also presented to provide context. Monitoring results for both sport fish and water were generally comparable to historic observations.
For the next several years, annual monitoring of sport fish will be conducted to firmly establish baseline concentrations and interannual variation in support of monitoring of long-term trends as an essential performance measure for the TMDL. Monitoring of water will solidify the linkage analysis (the quantitative relationship between methylmercury in water and methylmercury in sport fish) in the TMDL. Water monitoring will also provide data that will be useful in verifying patterns and trends predicted by numerical models of mercury transport and cycling being developed for the Delta and Yolo Bypass by the California Department of Water Resources (DWR).
Mercury and Methylmercury in North Bay Tidal Marshes. RMP Mercury Coordination Meeting: Oakland,Ca.2008.
Mercury and Methylmercury Processes in North San Francisco Bay Tidal Wetland Ecosystems. SFEI Contribution No. 449. San Francisco Estuary Institute: Oakland, CA.2008.
Mercury and Methylmercury Processes in North San Francisco Bay Tidal Wetland Ecosystems. CalFed with San Francisco Estuary Institute as primary contractor.2005.
Mercury and tidal wetland restoration. CalFED Journal . SFEI Contribution No. 339.2002.
Mercury and tidal wetland restoration. In Chapter 6 in Brown, L. (ed.). DRAFT CALFED Whitepaper on: Ecological Processes in Tidal Wetlands of the Sacramento-San Joaquin Estuary and Their Implications for Proposed Restoration Efforts of the Ecosystem Restoration Program.. Chapter 6 in Brown, L. (ed.). DRAFT CALFED Whitepaper on: Ecological Processes in Tidal Wetlands of the Sacramento-San Joaquin Estuary and Their Implications for Proposed Restoration Efforts of the Ecosystem Restoration Program.2000.
Mercury Concentrations and Loads in a Large River System Tributary to San Francisco Bay, California, USA. Environmental Toxicology and Chemistry.2009.
Mercury concentrations in coastal California precipitation: Evidence of local and trans-Pacific fluxes of mercury to North America. Journal of Geophysical Research - Atmospheres . SFEI Contribution No. 58.2003.
Mercury Contamination from Historic Mining in Water and Sediment, Guadalupe River and San Francisco Bay, CA. Geochemistry: Exploration, Environment, Analysis . SFEI Contribution No. 298.2003.
Mercury deposition in a tidal marsh downstream of the historic New Almaden mining district, CA. SFEI Contribution No. 286.2003.
Mercury Effects, Sources, and Control Measures. SFEI Contribution No. 20. San Francisco Estuary Institute: Richmond, CA.1996.
Mercury in biosentinel fish in San Francisco Bay: First-year project report. SFEI Contribution No. 520.2006.
Mercury in San Francisco Bay forage fish. San Francisco Estuary Institute: Oakland, Ca.2010.
Mercury in Sport Fish from the Delta Region (Task 2A). SFEI Contribution No. 252. San Francisco Estuary Institute / CALFED Final Project Report.: Oakland, CA. p 88 pp.2002.
Mercury in sport fish from the Sacramento-San Joaquin Delta region, California. Science of the Total Environment 66-75 . SFEI Contribution No. 537.2008.
Mercury Isotopes Link Mercury in San Francisco Bay Forage Fish to Surface Sediments. Environmental Science and Technology.2011.
Mercury-Selenium Effects on Reproductive Success of Forster's Terns in San Francisco Bay. USGS: Davis, California. p 26.2009.
Mercury speciation in the San Francisco Bay estuary. Marine Chemistry . SFEI Contribution No. 56.2003.
Metal contamination in San Francisco Bay waters: Historic perturbations, contemporary concentrations, and future considerations. San Francisco Bay: The Ecosystem(J.T. Rollibaugh, ed.)American Association for the Advancement of Science 173-188 . SFEI Contribution No. 12.1996.
Methods and Data for Analysis of Potential Distribution and Abundance of Zebra Mussels in California. SFEI Contribution No. 225. A report for CALFED and the California Urban Water Agencies. San Francisco Estuary Institute: Richmond CA.1998.
Methods for Analysis of Spatial and Temporal Patterns. SFEI Contribution No. 18. San Francisco Estuary Institute: Richmond, CA.1996.
Microbial degradation of penoxsulam in flooded rice field soils. Journal of Agricultural and Food Chemistry 54, 5962-5967.2006.
Microbial Water Quality at Minimally Human-Impacted Reference Beaches in Northern California. SFEI Contribution No. 858. San Francisco Estuary Institute : Richmond, CA.2018.
Microparticles, Microplastics, and PAHs in Bivalves in San Francisco Bay. SFEI Contribution No. 976. San Francisco Estuary Institute: Richmond, CA.2020.
California mussels (Mytilus californianus and hybrid Mytilus galloprovincialis / Mytilus trossulus) and Asian clams (Corbicula fluminea) were collected at multiple sites in San Francisco Bay. Mussels from a reference area with minimal urban influence were also deployed in cages for 90 days at multiple sites within the Bay prior to collection.Mussels from the reference time zero site, Bodega Head, had some of the lowest microparticle levels found in this study, along with resident clams from the San Joaquin and Sacramento Rivers and mussels transplanted to Pinole Point. The highest concentrations of microparticles were in mussels transplanted to Redwood Creek and Coyote Creek. The results of this study and current literature indicate that bivalves may not be good status and trends indicators of microplastic concentrations in the Bay unless the interest is in human health exposure via contaminated bivalve consumption.
Microplastic Contamination in San Francisco Bay - Fact Sheet. 2015, Revised 2016. SFEI Contribution No. 770.2016.
Microplastic contamination in the San Francisco Bay, California, USA. Marine Pollution Bulletin 109 . SFEI Contribution No. 769.2016.
Despite widespread detection of microplastic pollution in marine environments, data describing microplastic abundance in urban estuaries and microplastic discharge via treated municipal wastewater are limited. This study presents information on abundance, distribution, and composition of microplastic at nine sites in San Francisco Bay, California, USA. Also presented are characterizations of microplastic in final effluent from eight wastewater treatment plants, employing varying treatment technologies, that discharge to the Bay. With an average microplastic abundance of 700,000 particles/km2, Bay surface water appears to have higher microplastic levels than other urban waterbodies sampled in North America. Moreover, treated wastewater from facilities that discharge into the Bay contains considerable microplastic contamination. Facilities employing tertiary filtration did not show lower levels of contamination than those using secondary treatment. As textile-derived fibers were more abundant in wastewater, higher levels of fragments in surface water suggest additional pathways of microplastic pollution, such as stormwater runoff.
Microplastic Monitoring and Science Strategy for San Francisco Bay. SFEI Contribution No. 798. San Francisco Estuary Institute: Richmond, Calif.2017.
Microplastic pollution is widely detected in US municipal wastewater treatment plant effluent. Environmental Pollution 218, 1045-1054.2016.
Municipal wastewater effluent has been proposed as one pathway for microplastics to enter the aquatic environment. Here we present a broad study of municipal wastewater treatment plant effluent as a pathway for microplastic pollution to enter receiving waters. A total of 90 samples were analyzed from 17 different facilities across the United States. Averaging all facilities and sampling dates, 0.05 ± 0.024 microparticles were found per liter of effluent. Though a small value on a per liter basis, even minor municipal wastewater treatment facilities process millions of liters of wastewater each day, yielding daily discharges that ranged from ∼50,000 up to nearly 15 million particles. Averaging across the 17 facilities tested, our results indicate that wastewater treatment facilities are releasing over 4 million microparticles per facility per day. Fibers and fragments were found to be the most common type of particle within the effluent; however, some fibers may be derived from non-plastic sources. Considerable inter- and intra-facility variation in discharge concentrations, as well as the relative proportions of particle types, was observed. Statistical analysis suggested facilities serving larger populations discharged more particles. Results did not suggest tertiary filtration treatments were an effective means of reducing discharge. Assuming that fragments and pellets found in the effluent arise from the 'microbeads' found in many cosmetics and personal care products, it is estimated that between 3 and 23 billion (with an average of 13 billion) of these microplastic particles are being released into US waterways every day via municipal wastewater. This estimate can be used to evaluate the contribution of microbeads to microplastic pollution relative to other sources (e.g., plastic litter and debris) and pathways (e.g., stormwater) of discharge.
Microplastic Strategy Update. SFEI Contribution No. 951. San Francisco Estuary Institute: Richmond, CA.2019.
Based on the detection of microplastics in San Francisco Bay surface water and Bay Area wastewater effluent in 2015, the Regional Monitoring Program for Water Quality in San Francisco Bay (RMP) convened a Microplastic Workgroup (MPWG) in 2016 to discuss the issue, identify management information needs and management questions (MQs), and prioritize studies to provide information to answer these management questions. The MPWG meets annually to review on-going microplastic projects and to conduct strategic long-term planning in response to new information in this rapidly evolving field.
In this nascent field with new findings published almost daily, the Strategy is designed to be a living document that is updated periodically. This Strategy Update includes a short summary of recent findings from the San Francisco Bay Microplastics Project - a major monitoring effort in the Bay - and an updated multi-year plan based on the newly acquired knowledge and current management needs.
Microtechniques for the determination of nanomolar concentrations of trace elements in 10 ml of sediment porewater. Analytica Chimica Acta 328, 13-17 . SFEI Contribution No. 193.1996.
Mission Bay Historical Ecology Reconnaissance Study: Data Collection Summary (Technical Report). SFEI Contribution No. 777.2016.
The goals of the Mission Bay Historical Ecology Reconnaissance Study were to collect and compile high-priority historical
The goals of the Mission Bay Historical Ecology Reconnaissance Study were to collect and compile high-priority historical
data about the Mission Bay landscape, identify sources that could help to develop a deeper understanding of early
ecological conditions, and to identify future possible research directions based on the available data. This technical
memorandum is intended to document the archives consulted during the reconnaissance study, summarize the collected
and compiled data, and to identify potential next steps. A separate technical presentation to project staff and advisors will
summarize the preliminary findings and questions generated from a review of the historical dataset. Ultimately, this
research is intended to support the San Diego Audubon Society’s Mission Bay Wetlands Conceptual Restoration Plan (CRP)
and the ReWild Mission Bay project.
On Mitten Crabs and Lung Flukes, 16, No. 2.2003.
On Mitten Crabs and Lung Flukes. In IEP Newsletter. IEP Newsletter. Vol. 16, pp 48-51.2003.
Model Development Plan to Support Nutrient Management Decisions in San Francisco Bay. SFEI Contribution No. 705. Richmond, CA.2014.
A Model of Long-Term PCB Fate in San Francisco Bay. San Francisco Estuary Institute: Oakland.2008.
Monitoring and Results for El Cerrito Rain Gardens. San Francisco Estuary Institute: Richmond, CA.2012.
Monitoring for Non-indigenous Organisms. SFEI Contribution No. 385. San Francisco Estuary Institute: Oakland, CA.1998.
Monitoring of Toxic Contaminants in the San Francisco Bay-Delta: A Critical Review, Emphasizing Spatial and Temporal Trend Monitoring. SFEI Contribution No. 153. AHI: Richmond, CA. p 244.1988.
Monitoring of Toxic Contaminants in the San Francisco Bay-Delta: A Critical Review. SFEI Contribution No. 152.1988.
Monitoring the US West Coast: An Assessment of California’s Estuaries and the Pacific Ocean:Spatial Hierarchy and its Rationale. SFEI Contribution No. 120. San Francisco Estuary Institute: Oakland, CA.2002.
Monitoring Trace Organic Contamination in Central Valley Fish: Current Data and Future Steps. SFEI Contribution No. 99. San Francisco Estuary Institute: Oakland, CA.2004.
Mt. Wanda Historical Ecology Investigation. SFEI Contribution No. 743. San Francisco Estuary Institute - Aquatic Science Center: Richmond, CA. p 51.2015.
Multi-box mass balance model of PFOA and PFOS in different regions of San Francisco Bay. Chemosphere 252 . SFEI Contribution No. 986.2020.
We present a model to predict the long-term distribution and concentrations of perfluorooctanoic acid (PFOA) and perfluorooctanesulfonic acid (PFOS) in estuaries comprising multiple intercommunicated sub-embayments. To that end, a mass balance model including rate constants and time-varying water inputs was designed to calculate levels of these compounds in water and sediment for every sub-embayment. Subsequently, outflows and tidal water exchanges were used to interconnect the different regions of the estuary. To calculate plausible risks to population, outputs of the model were used as inputs in a previously designed model to simulate concentrations of PFOA and PFOS in a sport fish species (Cymatogaster aggregata). The performance of the model was evaluated by applying it to the specific case of San Francisco Bay, (California, USA), using 2009 sediment and water sampled concentrations of PFOA and PFOS in North, Central and South regions. Concentrations of these compounds in the Bay displayed exponential decreasing trends, but with different shapes depending on region, compound, and compartment assessed. Nearly stable PFOA concentrations were reached after 50 years, while PFOS needed close to 500 years to stabilize in sediment and fish. Afterwards, concentrations stabilize between 4 and 23 pg/g in sediment, between 0.02 and 44 pg/L in water, and between 7 and 104 pg/g wet weight in fish, depending on compound and region. South Bay had the greatest final concentrations of pollutants, regardless of compartment. Fish consumption is safe for most scenarios, but due to model uncertainty, limitations in monthly intake could be established for North and South Bay catches.
Multi-year water quality performance and mass accumulation of PCBs, mercury, methylmercury, copper and microplastics in a bioretention rain garden. Journal of Sustainable Water in the Built Environment 5 (4) . SFEI Contribution No. 872.2019.
A multiyear water quality performance study of a bioretention rain garden located along a major urban transit corridor east of San Francisco Bay was conducted to assess the efficacy of bioretention rain gardens to remove pollutants. Based on data collected in three years between 2012 and 2017, polychlorinated biphenyls (PCBs) and suspended sediment concentrations (SSCs) were reduced (>90%), whereas total mercury (Hg), methylmercury (MeHg), and copper (Cu) were moderately captured (37%, 49%, and 68% concentration reduction, respectively). Anthropogenic microparticles including microplastics were retained by the bioretention rain garden, decreasing in concentration from 1.6 particles/L to 0.16 particles/L. Based on subsampling at 50- and 150-mm intervals in soil cores from two areas of the unit, PCBs, Hg, and MeHg were all present at the highest concentrations in the upper 100 mm in the surface media layers. Based on residential screening concentrations, the surface media layer near the inlet would need to be removed and replaced annually, whereas the rest of the unit would need replacement every 8 years. The results of this study support the use of bioretention in the San Francisco Bay Area as one management option for meeting load reductions required by San Francisco Bay total maximum daily loads, and provide useful data for supporting decisions about media replacement and overall maintenance schedules.