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Salomon, M.; Dusterhoff, S. D.; Askevold, R. A.; Grossinger, R. M. 2016. San Francisquito Creek Baylands: Landscape Change Metrics Analysis. Flood Control 2.0. SFEI Contribution No. 784. San Francisco Estuary Institute - Aquatic Science Center: Richmond, CA. p 12.

Major Findings
Over the past 150 years, lower San Francisquito Creek and the adjacent baylands have been modified for the sake of land reclamation and flood control. This study focused on developing an understanding of the magnitude of habitat change since the mid-19th century through comparisons of key historical and contemporary landscape-scale habitat features, as well as several key landscape metrics that relate to ecological functions and landscape resilience. The major findings from the analyses conducted for this study are as follows:
• Historically, the San Francisquito Creek Baylands included a mosaic of habitat types, including an extensive tidal marsh plain with salt pannes and an expansive tidal channel network, a broad bay flat, and a relatively wide contiguous low-gradient tidal-terrestrial transition zone.
• Since the late 19th century, a combination of land reclamation and the inland migration of the shoreline has resulted in a 55% decrease in tidal marsh area, a 67% decrease in total tidal channel length, a 40% reduction in channel flat area, a 20% increase in bay flat area, and a 95% decrease in tidal-terrestrial transition zone length.
• Land reclamation has also resulted in the creation of new features that did not exist in the area historically including tidal lagoons, non-tidal open water features, and non-tidal wetlands.
 

Recommendations
The findings from this study provide insight into the drivers for and magnitude of habitat change within the San Francisquito Creek Baylands, and can therefore help inform climate-resilient approaches for regaining some of the lost landscape features and ecological functions. Specific management recommendations developed from the study findings are as follows:
• The dramatic decrease in tidal marsh area and associated tidal channel length since the mid-1800s make tidal marsh restoration a high priority. To make restored areas sustainable over the long-term, restoration should include reestablishing regular tidal inundation as well as reestablishing a connection with San Francisquito Creek and the delivery of freshwater and fine sediment. Restoration efforts should focus on large contiguous areas with minimal infrastructure and should ideally be done sometime over the next decade to ensure the restored areas will have a chance of surviving the sharp increase in the rate of sea level rise that is predicted to occur around 2030 (Goals Update 2015).
• Similarly, the dramatic decrease in the tidal-terrestrial transition zone makes it a high priority for any restoration vision for this area. The transition zone provides distinct ecological services and marsh migration space, and is in need of restoration throughout the South Bay. Since most of the upland land along the historical tidal-terrestrial transition zone is currently developed, near-term restoration efforts should focus on creating transition zone habitats on the bayside of flood risk management levees (Goals Update 2015).
• The landscape metrics used in this study (tidal habitat area, tidal channel length, and tidal-terrestrial interface length) can be used to help design resilient landscape restoration and adaptation strategies around the mouth of San Francisquito Creek. Specifically, the metrics can be used to assess the long-term ecological benefit associated with various processes-based restoration approaches (i.e., approaches that create habitat features and establish physical processes required for habitat resilience). Additional useful landscape metrics are being developed as part of the Resilient Silicon Valley project (see Robinson et al. 2015).

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Salop, P.; Shimabuku, I.; Davis, J.; Franz, A. 2018. 2018 Bivalve Retrieval Cruise Report. SFEI Contribution No. 920. San Francisco Estuary Institute : Richmond, CA.
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Salop, P.; Gunther, A.; Bell, D.; Cotsifas, J.; Gold, J.; Ogle, S. 2002. Episodic Ambient Water Toxicity in the San Francisco Estuary. SFEI Contribution No. 51. San Francisco Estuary Institute: Oakland, CA.
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Salop, P. 2018. 2018 RMP Bivalve Deployment Cruise Report. SFEI Contribution No. 903. San Francisco Estuary Institute : Richmond, CA.
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Salop, P.; Franz, A. 2018. 2018 RMP Sediment Cruise Report. SFEI Contribution No. 907. San Francisco Estuary Institute : Richmond, CA.
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Salop, P.; Gunther, A. J.; Bell, D.; Cotsifas, J.; Gold, J.; Ogle, S. R. 2001. San Francisco Bay Episodic Toxicity Report - 2000. SFEI Contribution No. 233. San Francisco Estuary Institute: Richmond, CA.
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Salop, P.; Bell, D.; Gold, J. 1999. Field Sampling Manual for the RMP for Trace Substances (version 1, January 1999). SFEI Contribution No. 324. San Francisco Estuary Institute: Richmond, CA.
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Salop, P. 2017. 2017 RMP Water Cruise Report. SFEI Contribution No. 846. Applied Marine Sciences: Livermore, CA.
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Salop, P.; Herrmann, C. 2019. 2019 RMP Water Cruise Report. SFEI Contribution No. 967. Applied Marine Sciences: Livermore, CA.

This report details activities associated with the annual Regional Monitoring Program for Water Quality in the San Francisco Estuary (RMP) water cruise. The RMP water sampling program was redesigned in 2002 to adopt a randomized sampling design at thirty-one sites in place of the twenty-six “spine of the Estuary” stations sampled previously. In 2007, the number of sites was decreased to twenty-two stations and it remains as such for 2019.

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Schiff, K.; Trowbridge, P. R.; Sherwood, E. T.; Tango, P.; Batiuk, R. A. 2016. Regional monitoring programs in the United States: Synthesis of four case studies from Pacific, Atlantic, and Gulf Coasts. Regional Studies in Marine Science 4.

Water quality monitoring is a cornerstone of environmental protection and ambient monitoring provides managers with the critical data they need to take informed action. Unlike site-specific monitoring that is at the heart of regulatory permit compliance, regional monitoring can provide an integrated, holistic view of the environment, allowing managers to obtain a more complete picture of natural variability and cumulative impacts, and more effectively prioritize management actions. By reviewing four long-standing regional monitoring programs that cover portions of all three coasts in the United States–Chesapeake Bay, Tampa Bay, Southern California Bight, and San Francisco Bay–important insights can be gleaned about the benefits that regional monitoring provides to managers. These insights include the underlying reasons that make regional monitoring programs successful, the challenges to maintain relevance and viability in the face of ever-changing technology, competing demands and shifting management priorities. The lessons learned can help other managers achieve similar successes as they seek to establish and reinvigorate their own monitoring programs.

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Schoellhamer, D.; McKee, L.; Pearce, S.; Kauhanen, P.; Salomon, M.; Dusterhoff, S.; Grenier, L.; Marineau, M.; Trowbridge, P. 2018. Sediment Supply to San Francisco Bay. SFEI Contribution No. 842. San Francisco Estuary Institute : Richmond, CA.
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Schoellhamer, D. H. 1996. Factors affecting suspended-solids concentrations in South San Francisco Bay, California. Journal of Geophysical Research 101, 12,087-12,095 . SFEI Contribution No. 10.
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Applied Marine Sciences. 2015. 2015 RMP Water Cruise Plan. Applied Marine Sciences: Livermore, CA.
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Applied Marine Sciences. 2015. 2015 RMP Water Cruise Report. Applied Marine Sciences: Livermore, CA.
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Applied Marine Sciences. 2022. 2021 RMP Water Cruise Report. SFEI Contribution No. 1098. Applied Marine Sciences: Livermore, CA.

This report details activities associated with the biannual Regional Monitoring Program for Water Quality in the San Francisco Estuary (RMP) water cruise. The RMP water sampling program was redesigned in 2002 to adopt a randomized sampling design at thirty-one sites in place of the twenty-six “spine of the Estuary” stations sampled previously. In 2007, the number of sites was decreased to twenty-two stations, combined probabilistic and historic, and it remains as such for 2021. 

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Applied Marine Sciences. 2014. 2013 RMP Water Cruise Plan. Applied Marine Sciences: Livermore, CA.
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RMP Lead Scientist. 2015. 2015 RMP Artesian Slough Sampling & Analysis Plan. San Francisco Estuary Institute: Richmond, CA.
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Sedlak, M.; Sutton, R.; Wong, A.; Lin, D. 2018. Per and Polyfluoroalkyl Substances (PFAS) in San Francisco Bay: Synthesis and Strategy. SFEI Contribution No. 867. San Francisco Estuary Institute : Richmond, CA.
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Sedlak, M.; Sutton, R.; Miller, L.; Lin, D. 2019. Microplastic Strategy Update. SFEI Contribution No. 951. San Francisco Estuary Institute: Richmond, CA.

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.

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Sedlak, M.; Greig, D. 2012. Perfluoroalkyl compounds (PFCs) in wildlife from an urban estuary. Journal of Environmental Monitoring 14, 146-154.
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Senn, D. B.; Novick, E. 2014. Suisun Bay Ammonium Synthesis. SFEI Contribution No. 706. San Francisco Estuary Institute: Richmond, CA. p 191.
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Senn, D.; Novick, E. 2016. Nutrient Management Strategy Science Plan Report. SFEI Contribution No. 878. San Francisco Estuary Institute: Richmond, CA.
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Senn, D.; Trowbridge, P. 2016. San Francisco Bay Nutrient Management Strategy Observation Program. SFEI Contribution No. 877. San Francisco Estuary Institute: Richmond, CA.
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2021. 2020-21 RMP North Bay Selenium Study. SFEI Contribution No. 1052. San Francisco Estuary Institute: Richmond, CA.

This report details activities associated with the Regional Monitoring Program North Bay Selenium Study in 2020 and 2021. The study was designed to monitor two sites for selenium (Se) in water and clam tissue six times annually between June and February. Due to the COVID pandemic, however, four sample collection events were completed. This report outlines the sampling activities, personnel, and site locations monitored for the project.

 

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2020. 2019-20 RMP North Bay Selenium Study. 2019-20 RMP North Bay Selenium Study. SFEI Contribution No. 1051. San Francisco Estuary Institute: Richmond, CA.

This report details activities associated with the Regional Monitoring Program North Bay Selenium Study. The  study was designed to monitor two sites for selenium (Se) in clam tissues and water six times between June  2019 and February 2020. This report outlines the sampling activities, personnel, and site locations monitored for  the project. 

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SFEI. 2007. 2007 Pulse of the Estuary: Monitoring and Managing Water Quality in the San Francisco Estuary. SFEI Contribution No. 532. San Francisco Estuary Institute: Oakland, CA. p 88.
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SFEI; Safran, S. M. 2014. Natural Flow Hydrodynamic Modeling Technology Support Phase 1 Technical Memorandum.

This technical memorandum summarizes the work to date carried out by the San Francisco Estuary Institute (SFEI) to generate a bathymetric-topographic digital elevation model (DEM) of the historical Sacramento-San Joaquin Delta (representative of early 1800s conditions). The historical DEM described in this document is an interim/draft product completed for Phase I of the Bay-Delta Natural Flow Hydrodynamics and Salinity Transport modeling project. It is expected that the product and methods described here will be refined during a second phase of the project.

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SFEI. 2003. 2003 Pulse of the Estuary: Monitoring & Managing Contamination in the San Francisco Estuary. SFEI Contribution No. 74. San Francisco Estuary Institute : Oakland, CA.
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SFEI. 2001. 1993 - 1999 Pulse of the Estuary: Monitoring and Managing Contamination in the San Francisco Estuary. SFEI Contribution No. 101. San Francisco Estuary Institute: Oakland, CA.
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SFEI; ESA,; Baye, P. 2023. Growing Resilience: Recommendations for Dune Management at North Ocean Beach. SFEI Contribution No. 1155. San Francisco Estuary Institute: Richmond, CA.
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SFEI. 2004. 2004 Pulse of the Estuary: Monitoring & Managing Contamination in the San Francisco Estuary. SFEI Contribution No. 401. San Francisco Estuary Institute : Oakland, CA.
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SFEI. 2005. 2005 Pulse of the Estuary: Monitoring and Managing Water Quality in the San Francisco Estuary. SFEI Contribution No. 78. San Francisco Estuary Institute: Oakland, CA. p 84.
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SFEI. 2016. 2015 Annual Monitoring Report. SFEI Contribution No. 775. San Francisco Estuary Institute: Richmond, CA.
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SFEI. 2017. The Pulse of the Bay: The 25th Anniversary of the RMP. SFEI Contribution No. 841. San Francisco Estuary Institute: Richmond, CA.
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SFEI. 2008. 2008 Pulse of the Estuary: Monitoring and Managing Water Quality in the San Francisco Estuary. SFEI Contribution No. 559. San Francisco Estuary Institute: Oakland, CA.
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SFEI. 2009. 2009 Pulse of the Estuary: Bay Sediments - Past a Tipping Point. SFEI Contribution No. 583. San Francisco Estuary Institute: Oakland, CA. p 92.
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SFEI. 2013. 2013 Pulse of the Bay: Contaminants of Emerging Concern. San Francisco Estuary Institute : Richmond, CA. p 102.
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SFEI. 2015. 2015 Pulse of the Bay: The State of Bay Water Quality - 2015 and 2065. SFEI Contribution No. 759. San Francisco Estuary Institute: Richmond, CA.
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SFEI. 2023. Landscape Scenario Planning Tool User Guide v2.2.0. San Francisco Estuary Institute: Richmond, Calif.
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SFEI. 2010. 2010 Pulse of the Estuary: Linking the Watersheds and the Bay. SFEI Contribution No. 618. San Francisco Estuary Institute : Oakland, CA. p 96.
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SFEI. 2012. 2011 Pulse of the Estuary: Pollutant Effects on Aquatic Life. SFEI Contribution No. 660. San Francisco Estuary Institute : Richmond, CA. p 104.
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SFEI. 2015. 2015 Sturgeon Muscle Plug Study Sampling & Analysis Plan. San Francisco Estuary Institute : Richmond, CA.
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SFEI. 2016. 2016 RMP Sturgeon Derby Study Sampling & Analysis Plan. San Francisco Estuary Institute : Richmond, CA.
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SFEI. 2006. The 2004 to 2005 RMP Annual Monitoring Results. Regional Monitoring Program for Water Quality in the San Francisco Estuary (RMP). SFEI Contribution No. 519. San Francisco Estuary Institute. p 220.
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SFEI; CDHS,. 2001. The San Francisco Bay Seafood Consumption Study Report. SFEI Contribution No. 369. San Francisco Estuary Institute: Oakland, CA.
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SFEI. 2021. Ecotone levees and wildlife connectivity: A technical update to the Adaptation Atlas. SFEI Contribution No. 1037. San Francisco Estuary Institute: Richmond, CA.
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SFEI. 2019. The Pulse of the Bay 2019: Pollutant Pathways. SFEI Contribution No. 954. San Francisco Estuary Institute: Richmond, CA.
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Shimabuku, I.; Trowbridge, P.; Salop, P.; Franz, A. 2018. 2018 RMP Bivalve Retrieval Cruise Plan. SFEI Contribution No. 893. San Francisco Estuary Institute : Richmond, CA.
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Shimabuku, I.; Trowbridge, P.; Salop, P. 2018. 2018 RMP Bivalve Retrieval Cruise Plan. SFEI Contribution No. 893. San Francisco Estuary Institute: Richmond, CA.
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Shimabuku, I.; Trowbridge, P.; Salop, P. 2018. 2018 RMP Bivalve Deployment Cruise Plan. SFEI Contribution No. 892. San Francisco Estuary Institute: Richmond, CA.
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