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C
Cohen, A. N. 1998. The invasion of the Pacific Coast by the European green crab. Eighth International Zebra Mussel and Aquatic Nuisance Species Conference, Page 44.
Cohen, A. N. 1998. The exotic species threat to California's coastal resources. California and the World Ocean '97, 1418-1426.
Cohen, A. N. 1999. Invasions status and policy on the U. S. west coast. First National Conference on Marine Bioinvasion, 40-45.
Cohen, A. N. 1997. Biological invasions in the San Francisco Estuary. Ann. Mtg., American Fisheries Society, Aug 24-28, Monterey CA (abstract)..
Cohen, A. N. 1996. Damming the Bay. Watershed 35, 6-8.
Cohen, A. N. 1993. Place Invaders. Pacific Discovery (Calif. Acad. Sci.) 46, 22-26.
Cohen, A. N. 1992. Weeding the Garden. Atlantic Monthly 270, 76-86.
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Cloern, J. E.; Cole, B. E.; Jassby, A. D. 1997. The design of sampling transects for characterizing water quality in estuaries. Estuarine, Coastal and Shelf Science 45, 285-302 . SFEI Contribution No. 23.
Cloern, J. E.; Robinson, A.; Richey, A.; Grenier, J. Letitia; Grossinger, R. M.; Boyer, K. E.; Burau, J.; Canuel, E.; DeGeorge, J. F.; Drexler, J. Z.; et al. 2016. Primary Production in the Delta: Then and Now. San Francisco Estuary and Watershed Science 14 (3).

To evaluate the role of restoration in the recovery of the Delta ecosystem, we need to have clear targets and performance measures that directly assess ecosystem function. Primary production is a crucial ecosystem process, which directly limits the quality and quantity of food available for secondary consumers such as invertebrates and fish. The Delta has a low rate of primary production, but it is unclear whether this was always the case. Recent analyses from the Historical Ecology Team and Delta Landscapes Project provide quantitative comparisons of the areal extent of 14 habitat types in the modern Delta versus the historical Delta (pre-1850). Here we describe an approach for using these metrics of land use change to: (1) produce the first quantitative estimates of how Delta primary production and the relative contributions from five different producer groups have been altered by large-scale drainage and conversion to agriculture; (2) convert these production estimates into a common currency so the contributions of each producer group reflect their food quality and efficiency of transfer to consumers; and (3) use simple models to discover how tidal exchange between marshes and open water influences primary production and its consumption. Application of this approach could inform Delta management in two ways. First, it would provide a quantitative estimate of how large-scale conversion to agriculture has altered the Delta's capacity to produce food for native biota. Second, it would provide restoration practitioners with a new approach—based on ecosystem function—to evaluate the success of restoration projects and gauge the trajectory of ecological recovery in the Delta region.

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Cloern, J. E.; Safran, S. M.; Vaughn, L. Smith; Robinson, A.; Whipple, A.; Boyer, K. E.; Drexler, J. Z.; Naiman, R. J.; Pinckney, J. L.; Howe, E. R.; et al. 2021. On the human appropriation of wetland primary production. Science of the Total Environment 785.

Humans are changing the Earth's surface at an accelerating pace, with significant consequences for ecosystems and their biodiversity. Landscape transformation has far-reaching implications including reduced net primary production (NPP) available to support ecosystems, reduced energy supplies to consumers, and disruption of ecosystem services such as carbon storage. Anthropogenic activities have reduced global NPP available to terrestrial ecosystems by nearly 25%, but the loss of NPP from wetland ecosystems is unknown. We used a simple approach to estimate aquatic NPP from measured habitat areas and habitat-specific areal productivity in the largest wetland complex on the USA west coast, comparing historical and modern landscapes and a scenario of wetland restoration. Results show that a 77% loss of wetland habitats (primarily marshes) has reduced ecosystem NPP by 94%, C (energy) flow to herbivores by 89%, and detritus production by 94%. Our results also show that attainment of habitat restoration goals could recover 12% of lost NPP and measurably increase carbon flow to consumers, including at-risk species and their food resources. This case study illustrates how a simple approach for quantifying the loss of NPP from measured habitat losses can guide wetland conservation plans by establishing historical baselines, projecting functional outcomes of different restoration scenarios, and establishing performance metrics to gauge success.

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Cloern, J. E.; Barnard, P. L.; Beller, E. E.; Callaway, J.; Grenier, J. Letitia; Grossinger, R. M.; Whipple, A.; Mooney, H.; Zavaleta, E. 2016. Estuaries: Life on the edge. In Ecosystems of California. Ecosystems of California. University of California Press: Berkeley, CA. pp 359-388.
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Clark, S.; Bailey, H. C.; Davis, J. A. 1995. The Effects of Toxic Contaminants in Waters of the San Francisco Bay and Delta. SFEI Contribution No. 184. Prepared for Bay/Delta Oversight Council: Sacramento, CA. p 125 pp.
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Chang, D.; Richardot, W.; Miller, E.; Dodder, N.; Sedlak, M.; Hoh, E.; Sutton, R. 2021. Framework for nontargeted investigation of contaminants released by wildfires into stormwater runoff: Case study in the northern San Francisco Bay area. Integrated Environmental Assessment and Management . SFEI Contribution No. 1044.

Wildfires can be extremely destructive to communities and ecosystems. However, the full scope of the ecological damage is often hard to assess, in part due to limited information on the types of chemicals introduced to affected landscapes and waterways. The objective of this study was to establish a sampling, analytical, and interpretive framework to effectively identify and monitor contaminants of emerging concern in environmental water samples impacted by wildfire runoff. A nontargeted analysis consisting of comprehensive two-dimensional gas chromatography coupled to time-of-flight mass spectrometry (GC × GC/TOF-MS) was conducted on stormwater samples from watersheds in the City of Santa Rosa and Sonoma and Napa Counties, USA, after the three most destructive fires during the October 2017 Northern California firestorm. Chemicals potentially related to wildfires were selected from the thousands of chromatographic features detected through a screening method that compared samples from fire-impacted sites versus unburned reference sites. This screening led to high confidence identifications of 76 potentially fire-related compounds. Authentic standards were available for 48 of these analytes, and 46 were confirmed by matching mass spectra and GC × GC retention times. Of these 46 compounds, 37 had known commercial and industrial uses as intermediates or ingredients in plastics, personal care products, pesticides, and as food additives. Nine compounds had no known uses or sources and may be oxidation products resulting from burning of natural or anthropogenic materials. Preliminary examination of potential toxicity associated with the 46 compounds, conducted via online databases and literature review, indicated limited data availability. Regional comparison suggested that more structural damage may yield a greater number of unique, potentially wildfire-related compounds. We recommend further study of post-wildfire runoff using the framework described here, which includes hypothesis-driven site selection and nontargeted analysis, to uncover potentially significant stormwater contaminants not routinely monitored after wildfires and inform risk assessment. 

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Carlton, J. T. 1996. The Invaded estuary (abstract). In In: Third Biennial State of the Estuary Conf.. In: Third Biennial State of the Estuary Conf. San Francisco, CA.
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Buzby, N.; Yee, D.; Foley, M.; David, J.; Sigala, M.; Bonnema, A. 2020. 2019 Sport Fish Monitoring Sampling and Analysis Plan. SFEI Contribution No. 970. San Francisco Estuary Institute: Richmond, CA.

The Regional Monitoring Program for Water Quality in San Francisco Bay (RMP) monitors concentrations of contaminants in fish tissue as indicators of bioaccumulation of contaminants in the Bay. In 2019, the RMP will conduct its eighth round of sport fish monitoring by collecting sport fish samples from various locations in the Bay as a part of routine Status and Trends Monitoring. Add-ons to the routine Status and Trends sport fish monitoring design will include archiving for microplastics and fipronil, as well as additional collections of shiner surfperch in Priority Margin Unit areas (PMUs).

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Buzby, N.; Lin, D.; Sutton, R. 2020. Neonicotinoids and Their Degradates in San Francisco Bay Water. SFEI Contribution No. 1002. San Francisco Estuary Institute: Richmond, CA.

In the summer of 2017, open Bay water samples were collected during the RMP Status and Trends Water Cruise. Samples were analyzed for 19 neonicotinoids and metabolites. The only neonicotinoid detected was imidacloprid, an active ingredient used in both urban and agricultural applications. Imidacloprid was detected at a single site above the method detection limits (2.2-2.6 ng/L) in Lower South Bay at a level of 4.2 ng/L. This value is within the range of concentrations found in a separate RMP study in water samples collected from the South and Lower South Bay margins in 2017. Imidacloprid was detected at 3 of 12 of the margin sites at levels between 3.9 and 11 ng/L; no other neonicotinoids were detected. Of note, these RMP studies appear to represent the first evaluation of ambient neonicotinoid concentrations in an estuarine environment in the nation.

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Buzby, N.; Yee, D.; Salop, P.; Foley, M. 2020. 2019 RMP North Bay Selenium Monitoring Sampling and Analysis Plan. SFEI Contribution No. 969. San Francisco Estuary Institute: Richmond, CA.

The goal of monitoring for selenium in the North Bay tissue and water is to identify leading indicators of change to allow prompt management response to signs of increasing impairment. At the 2016 technical workshop, participants reached a consensus that monitoring sturgeon, clams, and water are all needed to answer management questions. Recommendations for long-term monitoring of these three matrices are detailed in the North Bay Monitoring Design document (Grieb et al. 2018). The purpose of this Sampling and Analysis Plan is to clearly document the sampling design, methods, and responsibilities; and to facilitate coordination among project partners.

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Buchanan, P. A.; Schoellhamer, D. H. 1996. Summary of Suspended-Solids Concentration Data, San Francisco Bay, California, Water Year 1995. SFEI Contribution No. 13. US Geological Survey Open-File Report. pp 96-591.
Buchanan, P. A.; Ganju, N. K. 2002. Summary of Suspended-Sediment Concentration Data, San Francisco Bay, California, Water Year 2000. SFEI Contribution No. 242. US Geological Survey Open-File Report. pp 96-591.
Bruland, K. W.; Anderson, L. A. 1991. Biogeochemistry of arsenic in natural waters: The importance of methylated species. Environmental Science & Technology 25, 420-427 . SFEI Contribution No. 160.
Bruland, K. W.; Miller, L. A. 1995. Organic speciation of silver in marine waters. Environmental Science and Technology 29, 2616-2621 . SFEI Contribution No. 186.
Bruland, K. W.; Phinney, J. T. 1994. Uptake of lipophilic organic Cu, Cd, and Pb complexes in the coastal diatom, Thalassiosira Weissflogii. Environmental Science and Technology 28, 1781-1790 . SFEI Contribution No. 179.
Brewster, E. 2006. Land Grant Research and the Pictorial Collection. In Exploring the Bancroft Library. Exploring the Bancroft Library. The Bancroft Library/Signature Books. Vol. In Faulhab, p 196.
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Brander, S. M.; Renick, V. C.; Foley, M. M.; Steele, C.; Woo, M.; Lusher, A.; Carr, S.; Helm, P.; Box, C.; Cherniak, S.; et al. 2020. Sampling and Quality Assurance and Quality Control: A Guide for Scientists Investigating the Occurrence of Microplastics Across Matrices. Applied Spectroscopy 74 (9) . SFEI Contribution No. 1012.

Plastic pollution is a defining environmental contaminant and is considered to be one of the greatest environmental threats of the Anthropocene, with its presence documented across aquatic and terrestrial ecosystems. The majority of this plastic debris falls into the micro (1 lm–5 mm) or nano (1–1000 nm) size range and comes from primary and secondary sources. Its small size makes it cumbersome to isolate and analyze reproducibly, and its ubiquitous distribution creates numerous challenges when controlling for background contamination across matrices (e.g., sediment, tissue, water, air). Although research on microplastics represents a relatively nascent subfield, burgeoning interest in questions surrounding the fate and effects of these debris items creates a pressing need for harmonized sampling protocols and quality control approaches. For results across laboratories to be reproducible and comparable, it is imperative that guidelines based on vetted protocols be readily available to research groups, many of which are either new to plastics research or, as with any new subfield, have arrived at current approaches through a process of trial-and-error rather than in consultation with the greater scientific community. The goals of this manuscript are to (i) outline the steps necessary to conduct general as
well as matrix-specific quality assurance and quality control based on sample type and associated constraints, (ii) briefly review current findings across matrices, and (iii) provide guidance for the design of sampling regimes. Specific attention is paid to the source of microplastic pollution as well as the pathway by which contamination occurs, with details provided regarding each step in the process from generating appropriate questions to sampling design and collection.

Box, C.; Cummins, A. 2019. San Francisco Bay Microplastics Project: Science-Supported Solutions and Policy Recommendations. SFEI Contribution No. 955. 5 Gyres: Los Angeles, CA.

Plastics in our waterways and in the ocean, and more specifically microplastics (plastic particles less than 5 mm in size), have gained global attention as a pervasive and preventable threat to marine ecosystem health. The San Francisco Bay Microplastics Project was designed to provide critical data on microplastics in the Bay Area. The project also engaged multiple stakeholders in both science and policy discussions. Finally, the project was designed to generate scientifically supported regional and statewide policy recommendations for solutions to plastic pollution.

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Bigelow, P.; Pearce, S.; McKee, L. J. . 2009. Dry Creek Watershed Sediment Source Reconnaissance Technical Memorandum. SFEI Contribution No. 595. San Francisco Estuary Institute: Oakland,Ca.
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Bigelow, P.; Pearce, S.; McKee, L. J. .; Gilbreath, A. N. 2008. A Sediment Budget for Two Reaches of Alameda Creek. SFEI Contribution No. 550. San Francisco Estuary Institute.
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Berger, R.; Conomos, J.; Herrgesell, P.; Mearns, A.; Schubel, J. R.; Weisberg, S. 2004. Report of the 2003 Program Review. SFEI Contribution No. 303. San Franciso Estuary Institute: Oakland.
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Beller, E. E.; Spotswood, E.; Robinson, A.; Anderson, M. G.; Higgs, E. S.; Hobbs, R. J.; Suding, K. N.; Zavaleta, E. S.; Grenier, L.; Grossinger, R. M. 2018. Building Ecological Resilience in Highly Modified Landscapes.

Ecological resilience is a powerful heuristic for ecosystem management in the context of rapid environmental change. Significant efforts are underway to improve the resilience of biodiversity and ecological function to extreme events and directional change across all types of landscapes, from intact natural systems to highly modified landscapes such as cities and agricultural regions. However, identifying management strategies likely to promote ecological resilience remains a challenge. In this article, we present seven core dimensions to guide long-term and large-scale resilience planning in highly modified landscapes, with the objective of providing a structure and shared vocabulary for recognizing opportunities and actions likely to increase resilience across the whole landscape. We illustrate application of our approach to landscape-scale ecosystem management through case studies from two highly modified California landscapes, Silicon Valley and the Sacramento–San Joaquin Delta. We propose that resilience-based management is best implemented at large spatial scales and through collaborative, cross-sector partnerships.

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Beller, E. E.; Salomon, M.; Grossinger, R. M. 2013. An Assessment of the South Bay Historical Tidal-Terrestrial Transition Zone. SFEI Contribution No. 693. San Francisco Estuary Institute: Richmond, CA.
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Beller, E. E.; Grossinger, R. M.; Whipple, A. 2009. Historical Ecology Reconnaissance for the Lower Salinas River. SFEI Contribution No. 581. San Francisco Estuary Institute: Richmond. p 32.
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Beller, E. E.; Downs, P. W.; Grossinger, R. M.; Orr, B. K.; Salomon, M. 2016. From past patterns to future potential: using historical ecology to inform river restoration on an intermittent California river. Landscape Ecology 31 (3), 20.

Context  Effective river restoration requires understanding a system’s potential to support desired functions. This can be challenging to discern in the modern landscape, where natural complexity and heterogeneity are often heavily suppressed or modified. Historical analysis is therefore a valuable tool to provide the long-term perspective on riverine patterns, processes, and ecosystem change needed to set appropriate environmental management goals and strategies.

Objective In this study, we reconstructed historical (early 1800s) riparian conditions, river corridor extent, and dry-season flow on the lower Santa Clara River in southern California, with the goal of using this enhanced understanding to inform restoration and management activities.

Method Hundreds of cartographic, textual, and visual accounts were integrated into a GIS database of historical river characteristics.

Results We found that the river was characterized by an extremely broad river corridor and a diverse mosaic of riparian communities that varied by reach, from extensive ([100 ha) willow-cottonwood forests to xeric scrublands. Reach-scale ecological heterogeneity was linked to local variations in dry-season water availability, which was in turn underpinned by regional geophysical controls on groundwater and surface flow.

Conclusions Although human actions have greatly impacted the river’s extent, baseflow hydrology, and riparian habitats, many ecological attributes persist in more limited form, in large part facilitated by these fundamental hydrogeological controls. By drawing on a heretofore untapped dataset of spatially explicit and long-term environmental data, these findings improve our understanding of the river’s historical and current conditions and allow the derivation of reach-differentiated restoration and management opportunities that take advantage of local potential.

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Beller, E. E.; Baumgarten, S.; Grossinger, R. M.; Longcore, T.; Stein, E. D.; Dark, S.; Dusterhoff, S. D. 2014. Northern San Diego County Lagoons Historical Ecology Investigation. SFEI Contribution No. 722. San Francisco Estuary Institute - Aquatic Science Center: Richmond, CA. p 215.
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Beller, E. E.; Robinson, A.; Grossinger, R. M.; Grenier, J. Letitia. 2015. Landscape Resilience Framework: Operationalizing Ecological Resilience at the Landscape Scale. SFEI Contribution No. 752. San Francisco Estuary Institute - Aquatic Science Center: Richmond, CA.
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Beagle, J.; Salomon, M.; Grossinger, R. M.; Baumgarten, S.; Askevold, R. A. 2015. Shifting Shores: Marsh Expansion and Retreat in San Pablo Bay. SFEI Contribution No. 751.

EXECUTIVE SUMMARY
As sea level rise accelerates, our shores will be increasingly vulnerable to erosion. Particular concern centers around the potential loss of San Francisco Bay’s much-valued tidal marshes, which provide natural flood protection to our shorelines, habitat for native wildlife, and many other ecosystem services. Addressing this concern, this study is the first systematic analysis of the rates of marsh retreat and expansion over time for San Pablo Bay, located in the northern part of San Francisco Bay.

Key findings:
• Over the past two decades, more of the marshes in San Pablo Bay have expanded (35% by length) than retreated (6%).
• Some areas have been expanding for over 150 years.
• Some marsh edges that appear to be retreating are in fact expanding rapidly at rates of up to 8 m/yr.
• Marsh edge change may be a useful indicator of resilience, identifying favorable sites for marsh persistence.
• These data can provide a foundation for understanding drivers of marsh edge expansion and retreat such as wind direction, wave energy, watershed sediment supply, and mudflat shape.
• This understanding of system dynamics will help inform management decisions about marsh restoration and protection.
• This study provides a baseline and method for tracking marsh edge response to current and future conditions, particularly anticipated changes in sea level, wave energy, and sediment supply.


Recommended next steps:
• This pilot study for San Pablo Bay marshes should be extended to other marshes in San Francisco Bay.
• These initial marsh expansion and retreat findings should be further analyzed and interpreted to improve our understanding of system drivers and identify management responses.
• A program for repeated assessment should be developed to identify and track changes in shoreline position, a leading indicator of the likelihood marsh survival.

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Beagle, J.; Richey, A.; Hagerty, S.; Salomon, M.; Askevold, R. A.; Grossinger, R. M.; Reynolds, P.; McClain, C.; Spangler, W.; Quinn, M.; et al. 2017. Sycamore Alluvial Woodland: Habitat Mapping and Regeneration Study. SFEI Contribution No. 816.

This study investigates the relative distribution, health, and regeneration patterns of two major stands of sycamore alluvial woodland (SAW), representing managed and natural settings. Using an array of ecological and geomorphic field analyses, we discuss site characteristics favorable to SAW health and regeneration, make recommendations for restoration and management, and identify next steps. Findings from this study will contribute to the acquisition, restoration, and improved management of SAW as part of the Santa Clara Valley Habitat Plan (VHP).

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Beagle, J.; Lowe, J.; McKnight, K.; Safran, S. M.; Tam, L.; Szambelan, S. Jo. 2019. San Francisco Bay Shoreline Adaptation Atlas: Working with Nature to Plan for Sea Level Rise Using Operational Landscape Units. SFEI Contribution No. 915. SFEI & SPUR: Richmond, CA. p 255.

As the climate continues to change, San Francisco Bay shoreline communities will need to adapt in order to build social and ecological resilience to rising sea levels. Given the complex and varied nature of the Bay shore, a science-based framework is essential to identify effective adaptation strategies that are appropriate for their particular settings and that take advantage of natural processes. This report proposes such a framework—Operational Landscape Units for San Francisco Bay.

Printed copies available for purchase from Amazon.

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Baumgarten, S.; Grossinger, R.; Bazo, M.; Benjamin, M. 2020. Re-Oaking North Bay. SFEI Contribution No. 947. San Francisco Estuary Institute: Richmond, CA.
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Baumgarten, S. A. 2022. Ecological Horticulture at the Presidio. Lee, V., Bazo, M., Spotswood, E., Eds.. SFEI Contribution No. 1080. San Francisco Estuary Institute: Richmond, Ca.

The Presidio of San Francisco—the nation’s largest urban national park—is located in an area of exceptional ecological diversity. Historically, many different habitat types thrived in the mix of windswept dunes, riparian forests, and curious dwarf oak woodlands that characterized this landscape. Many of these habitat types are rare today (and some were even rare in the region historically), and together they harbor a host of unique plants and animals.

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Baumgarten, S.; Clark, E.; Dusterhoff, S.; Grossinger, R. M.; Askevold, R. A. 2018. Petaluma Valley Historical Hydrology and Ecology Study. SFEI Contribution No. 861. San Francisco Estuary Institute: Richmond, CA.

This study reconstructs the historical landscape of the Petaluma River watershed and documents the major landscape changes that have taken place within the watershed over the past two centuries. Prior to Spanish and American settlement of the region, the Petaluma River watershed supported a dynamic and interconnected network of streams, riparian forests, freshwater wetlands, and tidal marshes. These habitats were utilized by a wide range of plant and animal species, including a number of species that are today listed as threatened or endangered such as Ridgway’s Rail, Black Rail, salt marsh harvest mouse, California red-legged frog, Central California Coast steelhead, and soft bird’s beak (CNDDB 2012, SRCD 2015). Agricultural and urban development beginning in the mid-1800s has significantly altered the landscape, degrading habitat for fish and wildlife and contributing to contemporary management challenges such as flooding, pollutant loading, erosion, and sedimentation. While many natural areas and remnant wetlands still exist throughout the watershed—most notably the Petaluma Marsh—their ecological function is in many cases seriously impaired and their long-term fate jeopardized by climate change and other stressors. Multi-benefit wetland restoration strategies, guided by a thorough understanding of landscape history, can simultaneously address a range of chronic management issues while improving the ecological health of the watershed, making it a better place to live for both people and wildlife.

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Baumgarten, S.; Grossinger, R. M.; Beller, E. E.; Trowbridge, W.; Askevold, R. A. 2017. 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.

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.

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Baumgarten, S.; Beller, E. E.; Grossinger, R. M.; Askevold, R. A. 2015. Mt. Wanda Historical Ecology Investigation. SFEI Contribution No. 743. San Francisco Estuary Institute - Aquatic Science Center: Richmond, CA. p 51.
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Barnard, P. L.; Schoellhamer, D. H.; Jaffe, B. E.; McKee, L. J. . 2013. Sediment transport in the San Francisco Bay Coastal System: An overview. Marine Geology Special Issue: A multi-discipline approach for understanding sediment transport and geomorphic evolution in an estuarine-coastal system.
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