The overarching AIS goal is that "Risks of aquatic invasive species invasions are substantially reduced, and their economic, ecological, and human health impacts are minimized. This goal is addressed through a series of performance and workload measures. The AIS Program provides funding for Aquatic Invasive Species Coordinators for each Region within the Service and their respective aquatic nuisance species activities. These coordinators work closely with the public and private sector to develop and implement invasive species projects. One of the primary initiatives of the program is the prevention of invasive species via boats through the "100th Meridian Initiative" (overseen by individual AIS regional coordinators). This initiative aims to prevent the spread of aquatic invasive species by boats personal watercraft and other pathways. Through boat inspections and boaters assessments along the 100th meridian, partners can learn how to prevent the spread of zebra mussels and other AIS via transport of boats and personal watercraft.
Invasive aquatic vegetation (IAV) is widespread in the Sacramento-San Joaquin Delta (Delta) and its change in coverage has been mapped at the species level using spectroscopy data collected once a year, from 2004 to 2008 and from 2014 to 2019. There was no funding to conduct a similar mapping campaign in 2020. This work aims to collect and analyze imagery in summer of 2020 to fulfill two main objectives. First is to inform the monitoring framework for aquatic vegetation put forth for the Interagency Ecological Program (IEP). Comparing spring and fall imagery of 2019 and the summer imagery of 2020, the project will evaluate which time period is ideal for optimal mapping of aquatic vegetation considering the logistical challenges of airborne imagery acquisition and the phenology of the species being mapped. The project will also contrast the pros and cons of the 3 proposed scenarios in the IEP monitoring framework: 1) two hyperspectral acquisitions a year (2019; “best case” scenario), 2) one acquisition a year (2020, “moderate” scenario) and 3) satellite data based monitoring (the Sentinel-2 study, “bare bones” scenario). The second objective of the project is to determine if the new treatment framework (new herbicide formulations and application schedules) is effective in controlling the old (Brazilian waterweed, water hyacinth) and newly added target weed species (water primrose, alligator weed) in the Delta ecosystem.
Invasive aquatic macrophytes (aquatic weeds) cover increased dramatically in the Sacramento-San Joaquin Delta (Delta) during the 2013-2015 drought and the 2021-2023 drought. This trend toward increasing dominance of these invasive aquatic weeds has profound implications for delta/marsh habitat, as aquatic weeds are known to significantly alter the physical environment by slowing water velocities, increasing water clarity, providing habitat for invasive fishes, and reducing open water habitat. These habitat effects are thought to negatively impact the endangered Delta Smelt and other pelagic species that rely on turbid, open water habitat. During the drought of 2021- 2023, aquatic weeds have continued to spread into new habitats, therefore there is an urgent need to identify effective control measures, which requires increased understanding of ecosystem responses to drought and associated environmental conditions in the waterways (e.g., water temperature, flow rates, turbidity, etc.), and specific control measures.
The work covered in this contract includes the 2021-2023 Emergency Drought Salinity Barrier Monitoring Plan mandated under DWR’s Incidental Take Permit. Research has focused on understanding invasion patterns in Franks Tract and contrasting them with patterns in channels surrounding Liberty Island and restoration sites. We also analyze Suisun marsh to assess the condition near the salinity drought barrier on Montezuma Slough, and its impacts across the length of Montezuma Slough and relate observed patterns to salinity conditions in Suisun Slough.
Extensive field work has been conducted throughout the Delta and in Suisun Marsh to acquire data that is used to train and evaluate remotely sensed maps of aquatic weed distribution and link these to measurements of water quality. This project extends the time period of continued mapping of aquatic vegetation in the Delta through summer of 2027, for a time series that goes back to 2004, covering 19 years of high spatial resolution hyperspectral imagery data. This dataset now encompasses the full range of hydrologic conditions that extend from wet years to extremely dry years which can potentially form the basis for interpreting causal relationships and changes in trait distributions of aquatic weeds. Aquatic weed mapping combined with an extensive field campaign within the Suisun Marsh extends the Suisun time series to seven years. This growing time series of vegetation maps for both the Delta and Suisun Marsh can be leveraged to look at the evolution of tidal wetland restoration sites developed by DWR’s Fish Restoration Program (FRP) as part of the Incidental Take Permit. This analysis covers construction to current time period to see if different restoration strategies (pre-planting, no pre-action, treating invasive species outside the site, etc.) have an impact on the growth and maturity of a site, invasibility, etc. Additionally, the full time series will be evaluated for trends related to weather/climate, water conditions, and management actions.
The California Department of Parks and Recreation, Division of Boating and Waterways (DBW) operates a control program for both floating and submerged IAV. This project is an IEP Synthesis effort that will integrate a historical and ongoing dataset of the Delta IAV coverage and DBW IAV treatment records for the past 14 years. This study seeks to determine if treatment efficacy differs across space (e.g., different habitat types) and time. It will assess the impact of IAV control effort on the distribution, growth rate, spread and persistence, and species richness and community composition of the IAV communities. Gaining such understanding on the relationship between IAV treatment and IAV distribution, coverage, and species composition is an urgent management issue for the Delta, given the sharp rise in coverage of IAV from 9000 acres in 2004 to 12,500 acres in 2014 and its likely impact on the shallow-water habitat.
The objectives of this study are:
1. What are the rates and patterns of spread for floating IAV? Do the rates of spread into water or marsh differ? Where do these floating IAV persist and what mechanisms can be linked to their ability of persistence? If there are specific locations that promote persistence, for example over-wintering nurseries, could they be targeted for removal?
2. Has treatment for both water primrose and water hyacinth been successful in reducing species cover over the last 15 years? If so, was treatment effective in reducing density, reducing growth rates, slowing down expansion, and therefore changing distribution of target species? Does treatment efficacy change over different habitats and through time?
3. Does herbicide control of target submerged IAV species reduce density, growth rates, slow down expansion and persistence, and change submerged community composition towards native species? Does treatment efficacy change over different habitats and through time? Does it change the patch size and distribution?
