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Estuaries are ecologically and economically important ecosystems but are threatened by non-native invasive species, including many species of submersed aquatic vegetation (SAV). Herbicides are the primary tool used to control SAV, but most field evaluations of herbicides have been conducted in lentic systems. Therefore, managers working in estuaries must base their SAV control programs largely on findings from systems fundamentally different from their own. We conducted a study in the Sacramento-San Joaquin Delta to determine efficacy of the widely used herbicide fluridone in an estuarine ecosystem. The primary goal of SAV removal was restoration of open water habitat for endangered Hypomesus transpacificus (Delta Smelt). Over 18 months and multiple sets of multi-week fluridone applications, we monitored concentrations of fluridone and responses by SAV across pairs of treated and reference sites. Fluridone concentrations in the water were generally below the 2–5 parts per billion required for SAV control. Monitoring demonstrated that these low water concentrations were likely due to dissipation by tides, despite use of pelleted fluridone formulations marketed for flowing water environments. Fluridone did, however, accumulate in sediment at concentrations hundreds of times higher than those measured in the water. Nonetheless, we did not observe lasting reductions in SAV abundance or changes in SAV community composition. By demonstrating lack of efficacy of one of the few herbicides permitted for use in this estuary, this study highlights the need for development of SAV management tools tailored to the challenges of hydrologically complex environments like estuaries. [ABSTRACT FROM AUTHOR]

The Sacramento-San Joaquin Delta is one of the largest estuaries in North America, providing water for more than 700,000 acres of agriculture, recreation and fisheries habitat. For decades, the exotic invasive plant Egeria densa has negatively impacted native habitat and navigation of vessels in the Sacramento-San Joaquin Delta. In 2007 the largest waterbody in the Delta, Franks Tract, began to be managed at operational scale utilizing the aquatic herbicide fluridone. A fluridone pellet formulation was applied to achieve in-water concentrations of fluridone between 2.5 and 3.5 ppb for 8 to 16 weeks in areas with dense Egeria densa. Fluridone applications were started as early as March and continued throughout the treatment period to sustain the target concentrations which were verified by an enzyme-linked immunoassay (ELISA) analytical test. Relative frequency of occurrence for native plants significantly increased from 2006 to 2017 (P < 0.001). Frequency of occurrence of most native species remained variable across years except for Potamogeton richardsonii where frequency of occurrence increased greatly from 3.6% in 2013 to 80% in 2017 (P < 0.001), and significantly increased each year sequentially except between 2015 to 2016 to become the most widespread species. The increase of native plants over the past five years, following management with fluridone, is likely to improve fisheries, native species habitat, and waterway traffic. [ABSTRACT FROM AUTHOR]

The pathogenesis of experimental hepatitis E has not been thoroughly investigated. The purpose of this study was to more accurately document the events in this disease. Cynomolgus macaques were inoculated intravenously with bile or feces containing hepatitis E virus (HEV). Serum, bile, and liver specimens were evaluated with light microscopy, immune electron microscopy, immunofluorescence microscopy, EIA, and polymerase chain reaction. In the third week, there were histopathologic changes and HEV antigen (HEVAg) in liver, HEV in bile, and alanine aminotransferase (ALT) elevations. Widespread pathologic changes were detected during the fourth week and antibody to HEV (anti-HEV) and peak ALT values in the fifth or sixth week. By the sixth week, HEVAg had disappeared but pathologic changes persisted. This study supports the concept that experimental hepatitis E has an initial phase in which hepatic HEV replication is accompanied by the onset of hepatitis and a later phase in which the appearance ofanti-HEV is accompanied by progression of the hepatitis. [ABSTRACT FROM PUBLISHER]

Owl and cynomolgus monkeys were inoculated with hepatitis E virus (HEV) to compare disease models and produce antibody and virus. By immune electron microscopy (IEM), all six owl monkeys were shown to have serologic responses manifested by unusually high levels of antiHEV at 6 months, but only three developed hepatitis. Virus-related antigen in liver (HEVAg) was detected by immunofluorescence microscopy of biopsies from two of four owl monkeys; one with HEVAg also had HEV in acute-phase bile (detected by IEM) and feces (detected by infecting another owl monkey). In contrast, cynomolgus monkeys propagated HEV to higher levels and all five had hepatitis. Moderate-to-high levels of HEVAg correlated with detectable HEV in bile for both species. Thus, the value of using HEV-infected cynomolgus was confirmed. Owl monkeys were shown to be HEV-susceptible and sources of high-level anti-HEV; Sustained anti-HEV in these monkeys may also be useful for understanding immune responses. [ABSTRACT FROM PUBLISHER]

Fluridone is widely used as a herbicide for controlling invasive aquatic plants such as hydrilla in surface water bodies. When applied on surface waters fluridone can attach to bed sediment, requiring rigorous extraction methods prior to analysis. Currently, very limited information exists in terms of fluridone residue detection in delta sediment. In this study, we researched fluridone detection in both water and sediment. To extract fluridone from sediment, here we have tested two extraction methods: (1) a rotavapor method (RM); and (2) a quick, easy, cheap, effective, rugged and safe (QuEChERS) method (QM). The extraction results of RM were compared with those of QM. To quantify fluridone concentrations in extracts, a high-performance liquid chromatography (HPLC)-UV detector was used. HPLC separation was achieved using an Allure C18 5 µm 150 × 4.6 mm column with a mobile phase composed of acetonitrile and water (60:40, v/v). The UV detector was operated at 237 nm. The method was tested and validated using a series of water and sediment samples taken from Sacramento–San Joaquin Delta in California. The average recovery of fluridone was 73% and 78% using RM and QM respectively. The proposed method can be used for testing fluridone in water and sediment samples. [ABSTRACT FROM AUTHOR]