Our library features many hundreds of entries.
To search among them, click "Search" below to pull down options, including filtering by document type, author, year, and keyword.
Find these options under "Show only items where." Or you can also sort by author, title, type, and year clicking the headings below.
Green Infrastructure Planning for the City of Oakland with GreenPlan-IT. SFEI Contribution No. 884. San Francisco Estuary Institute : Richmond, CA.2018.
Green Infrastructure Planning for the City of Richmond with GreenPlan-IT. SFEI Contribution No. 883. San Francisco Estuary Institute: Richmond, CA.2018.
Green Infrastructure Planning for the City of Sunnyvale with GreenPlan-IT. SFEI Contribution No. 881. San Francisco Estuary Institute : Richmond, CA.2018.
Green Plan-IT Application Report for the East Bay Corridors Initiative. SFEI Contribution No. 887. San Francisco Estuary Institute: Richmond, CA.2018.
GreenPlan-IT Toolkit Demonstration Report. SFEI Contribution No. 958. San Francisco Estuary Institute: Richmond, CA.2015.
GreenPlan-IT is a planning level tool that was developed by SFEP and SFEI with support and oversight from BASMAA to provide Bay Area municipalities with the ability to evaluate multiple management alternatives using green infrastructure for addressing stormwater issues in urban watersheds. GreenPlan-IT combines sound science and engineering principles with GIS analysis and optimization techniques to support the cost-effective selection and placement of Green Infrastructure (GI) at a watershed scale. Tool outputs can be used to develop quantitatively-derived watershed master plans to guide future GI implementation for improving water quality in the San Francisco Bay and its tributary watersheds.
This report provides an overview of the GreenPlan-IT Tool and demonstrates its utility and power through two pilot studies which is summarized in this report as a case study. The pilot studies with the City of San Mateo and the City of San Jose explored the use of GreenPlan-IT for identifying feasible and optimal GI locations for mitigation of stormwater runoff. They are provided here to give the reader an overview of the user application process from start to finish, including problem formulation, data collection, GIS analysis, establishing a baseline condition, GI representation, and the optimization process. Through the pilot study application process the general steps and recommendations for how GreenPlan-IT can be applied and interpreted are presented.
GreenPlan-IT Toolkit User Guide. SFEI Contribution No. 958. San Francisco Estuary Institute: Richmond, CA.2015.
Structurally, the GreenPlan-IT is comprised of three components: (a) a GIS-based Site Locator Tool to identify potential GI sites; (b) a Modeling Tool that quantifies anticipated watershed-scale runoff and pollutant load reduction from GI sites; and (c) an Optimization Tool that uses a cost-benefit analysis to identify the best combinations of GI types and number of sites within a watershed for achieving flow and/or load reduction goals. The three tool components were designed as standalone modules to provide flexibility and their interaction is either through data exchange, or serving as a subroutine to another tool. This user manual addresses each of the tools separately, though they are designed to complement each other.
This technical memo describes the purpose, functions, and structure associated with the newest addition to the GreenPlan-IT Toolset, the GreenPlan-IT Tracker. It also shares the opportunities for further enhancement and how the tool can operate in concert with existing resources. Furthermore, this memo describes a licensing plan that would permit municipalities to use the tool in an ongoing way that scales to their needs. The memo concludes with a provisional roadmap for the development of future features and technical details describing the tool’s platform and data structures.
Groundwater seepage into northern San Francisco Bay: implications for dissolved metals budgets. Wate Resources Research . SFEI Contribution No. 54.2002.
Guadalupe River Mercury Concentrations and Loads During the Large Rare January 2017 Storm. SFEI Contribution No. 837. San Francisco Estuary Institute : Richmond, CA.2018.
Guadalupe River Watershed Loading HSPF Model: Year 3 final progress report. SFEI: Richmond, CA.2011.
Guadalupe Watershed Model Year 1 Report. Oakland, CA.2009.
Gut Contents Analysis of Four Fish Species Collected in the San Leandro Bay RMP PCB Study in August 2016. SFEI Contribution No. 900. San Francisco Estuary Institute: Richmond, CA.2018.
Habitat-Related Benthic Macrofaunal Assemblages of Bays and Estuaries of the Western United States. Integrated Environmental Assessment and Management 8 (4), 638-648.2010.
Hacienda Avenue Bio-Infiltration Basins (Case Study - Fact Sheet). San Francisco Estuary Institute: Richmond, CA.2016.
Have claw, will travel. Aquatic Nuisance Species Digest 2, 1, 16-17. . SFEI Contribution No. 200.1997.
Hg L 3 XANES study of mercury methylation in shredded Eichhornia crassipes. Environmental Science and Technology.2008.
The hidden costs of California's water. In Life on the Edge: A Resource Guide to California's Endangered Wildlife. Life on the Edge: A Resource Guide to California's Endangered Wildlife. Biosystems Books: Santa Cruz, CA. pp 288-302.1994.
The highly invaded ecosystem of San Francisco Bay. Cawthron Institute, Nelson, New Zealand.2002.
Historical Ecology and Landscape Change in the Central Laguna de Santa Rosa. SFEI Contribution No. 820. San Francisco Estuary Institute - Aquatic Science Center: Richmond, CA.2017.
This study synthesizes a diverse array of data to examine the ecological patterns, ecosystem functions, and hydrology that characterized a central portion of the Laguna de Santa Rosa during the mid-19th century, and to analyze landscape changes over the past 150 years. The primary purpose of this study was to help guide restoration actions and other measures aimed at reducing nutrient loads within this portion of the Laguna de Santa Rosa watershed.
Historical Ecology of Lower San Francisquito Creek Phase 1. San Francisco Estuary Institute: Oakland, Ca.2009.
The Historical Ecology of Napa Valley: An Introduction. SFEI Contribution No. 557.2008.
Historical Ecology of the lower Santa Clara River, Ventura River, and Oxnard Plain: an analysis of terrestrial, riverine, and coastal habitats. SFEI Contribution No. 641. SFEI: Oakland.2011.
Historical Ecology of the McCormack-Williamson Tract: A Landscape Framework for Restoration. SFEI Contribution No. 674. Aquatic Science Center / San Francisco Estuary: Richmond, CA.. 2012.
The Historical Ecology of the Tijuana Estuary & River Valley (Restore America's Estuaries 2018 Conference Presentation).2018.
This talk was given at the 2018 Restore America's Estuary Conference in Long Beach, CA as part of a special session titled "Restoration Perspectives from the Tijuana River National Estuarine Research Reserve." It is based on information from the Tijuana River Valley Historical Ecology Investigation, a report published in 2017.
Though many areas of the binational Tijuana River watershed remain relatively undeveloped, land and water use changes over the past 200 years have resulted in significant ecological impacts, particularly in the more urbanized areas of the lower watershed. Drawing upon a diverse set of historical data, we reconstructed the ecological and hydrogeomorphic conditions of the lower Tijuana River valley prior to major Euro-American modification (ca. 1850) and documented major changes in habitat distribution and physical processes over this time. The river corridor, which was historically dominated by riparian scrub, today instead supports dense stands of riparian forest. The valley bottom surrounding the river corridor, which historically supported extensive seasonal wetlands, has largely been converted to drier habitat types and agricultural uses. The estuary, which historically supported large expanses of salt marsh and mudflat as well as seasonally dry salt flats, has retained much of its former extent and character, but has been altered by increased sediment input and other factors. The new information about the historical landscape presented here is relevant to a number of issues scientists and managers are dealing with today, including the conservation of endangered species, the fate of the valley’s riparian habitats after the recent invasion of invasive shot-hole borer beetles, and the effects on groundwater levels on native plant communities. We will also draw from other historical ecology studies conducted in Southern California to illustrate how the information about the past has been utilized to improve the functioning and resilience of nearby coastal ecosystems.
Presentation recording: available here.
Historical Ecology Reconnaissance for the Lower Salinas River. SFEI Contribution No. 581. San Francisco Estuary Institute: Richmond. p 32.2009.
Historical Evidence of Freshwater Effects on the Plan Form of Tidal Marshlands in the Golden Gate Estuary, University of California: Santa Cruz, p 130 pp.1995.
The Historical Geography and Biogeography of Tidal Salt Marshes (Abstract). San Francisco Estuary Institute.2002.
2005. Historical Landscape Analysis (full title to come from Robin). SFEI Contribution No. 396. San Francisco Estuary Institute.
Historical landscape ecology of an urbanized California valley: wetlands and woodlands in the Santa Clara Valley. Landscape Ecology 103-120.2007.
Historical Wetlands of the Southern California Coast: An Atlas of US Coast Survey T-sheets, 1851-1889. SFEI Contribution No. 586. SFEI: Oakland.2011.
How Creeks Meet the Bay: Changing Interfaces (Interactive web map).2014.
San Francisco Bay’s connections to local creeks are integral to its health. These fluvial-tidal (F-T) interfaces are the points of delivery for freshwater, sediment, contaminants, and nutrients. The ways in which the F-T interface has changed affect flooding dynamics, ecosystem functioning, and resilience to a changing climate. As the historical baylands have been altered, the majority of contemporary F-T interface types have changed leading to additional F-T interface types within the present-day landscape. Illustrations of each F-T interface type and methods for classification are available here.
This project is part of Flood Control 2.0. For further information please visit this project page.
Human influences on nitrogen and phosphorus concentrations in creek and river waters of the Napa and Sonoma watersheds, northern San Francisco Bay, California. SFEI Contribution No. 421. San Francisco Estuary Institute: Oakland.2005.
Hydrodynamic and Water Quality Model Calibration and Application in San Francisco Bay. SFEI Contribution No. 913. San Francisco Estuary Institute : Richmond, CA.2018.
Identification and emission factors of molecular tracers in organic aerosols from biomass burning: Part 3. Grasses. Applied Geochemistry 21 (6) . SFEI Contribution No. 491.2006.
Identification and evaluation of previously unknown organic contaminants in the San Francisco Estuary (1999-2001). SFEI Contribution No. 75. San Francisco Estuary Institute: Oakland, CA.2003.
Identification and evaluation of unidentified organic contaminants in the San Francisco Estuary. SFEI Contribution No. 45. San Francisco Estuary Institute: Oakland, CA.2002.
The impact of an invasive Atlantic cordgrass (Spartina alterniflora) on San Francisco Bay Song Sparrow populations: direct and indirect influence. In Terrestrial Vertebrates of Tidal Marshes: Evolution, Ecology and Conservation. Terrestrial Vertebrates of Tidal Marshes: Evolution, Ecology and Conservation. Silver Spring, MD.2002.
Impact of invasive Spartina alterniflora on song sparrow and marsh wren populations in San Francisco Bay salt marshes. Proceedings of the International Spartina Conference.2005.
Impacts from the Asian clam Potamocorbula amurensis. In National Management Plan. National Management Plan. National Invasive Species Council: Washington DC.2001.
Impacts of invasions in the Bay and Delta. Abs. Proc. 75th Ann. Mtg., Pac. Div. Amer. Assoc. Adv. Sci..1994.
Impacts of Nonindigenous Species on Subtidal Benthic Assemblages in the San Francisco Estuary. SFEI Contribution No. 329. p 16.1999.
Implementation Manual for the San Leandro Creek Watershed Awareness Program, 1993-1994. SFEI Contribution No. 177. San Francisco Estuary Institute: Richmond, Ca. p 75.1994.
Increases in Anthropogenic Gadolinium Anomalies and Rare Earth Element Concentrations in San Francisco Bay over a 20 Year Record. Environ. Sci. Technol. 50 (8).2016.
We evaluated both the spatial distribution of gadolinium (Gd) and other rare earth elements (REE) in surface waters collected in a transect of San Francisco Bay (SFB) and their temporal variations within the Bay over two decades. The REE were preconcentrated using the NOBIAS PA-1 resin prior to analysis by high-resolution inductively coupled plasma mass spectrometry. Measurements revealed a temporal increase in the Gd anomaly in SFB from the early 1990s to the present. The highest Gd anomalies were observed in the southern reach of SFB, which is surrounded by several hospitals and research centers that use Gd-based contrast agents for magnetic resonance imaging. Recent increases in that usage presumably contributed to the order of magnitude increase in anthropogenic Gd concentrations in SFB, from 8.27 to 112 pmol kg–1 over the past two decades, and reach the northeast Pacific coastal waters. These measurements (i) show that “exotic” trace elements used in new high-tech applications, such as Gd, are emerging contaminants in San Francisco Bay and that anthropogenic Gd concentrations increased substantially over a 20 year period; (ii) substantiate proposals that REE may be used as tracers of wastewater discharges and hydrological processes; and (iii) suggest that new public policies and the development of more effective treatment technologies may be necessary to control sources and minimize future contamination by REE that are critical for the development of new technologies, which now overwhelm natural REE anomalies.
Indicator Development and Framework for Assessing Indirect Effects of Sediment Contaminants. SFEI Contribution No. 524. San Francisco Estuary Institute.2007.
Indicators and Performance Measures for North Bay Watersheds. San Francisco Estuary Institute: Oakland, Ca.2010.
Indirect reduction of hexavalent chromium by copper in the presence of superoxide. Marine Chemistry 69, 33-41 . SFEI Contribution No. 335.2000.
The Influence of Chemical and Physical Factors on Macrobenthos in the San Francisco Estuary. SFEI Contribution No. 543.2008.
Influence of climate, geology, and humans on spatial and temporal variability in nutrient geochemistry in the sub-tropical Richmond River catchment, Australia. Marine and Freshwater Research 52, 235-248 . SFEI Contribution No. 232.2001.
Influence of Thermal Stratification on the Depth of Distribution of Pelagic Juvenile Rockfish of central California. Fishery Bulletin . SFEI Contribution No. 475.2002.
Initial Protocol to Identify and Delineate the Head of Tide Zone in San Francisco Bay Tributaries. SFEI Contribution No. 719. San Francisco Estuary Institute: Richmond, CA.2014.
Inspection for Live Marine Invertebrates in an Oyster Shell Pile at Drakes Bay Oyster Company. San Francisco Estuary Institute.2006.
Integrated Coastal Reserve Planning, Making the Land—Sea Connection. Front Ecol Environ 3 (8), 429-436.2005.