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Janet L. Miller

Researcher at United States Geological Survey

Publications -  5
Citations -  100

Janet L. Miller is an academic researcher from United States Geological Survey. The author has contributed to research in topics: Periphyton & Bioaccumulation. The author has an hindex of 4, co-authored 5 publications receiving 45 citations. Previous affiliations of Janet L. Miller include Colorado State University.

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Bioaccumulation and Toxicity of Cadmium, Copper, Nickel, and Zinc and Their Mixtures to Aquatic Insect Communities.

TL;DR: Testing translocated aquatic insect communities in 30‐d artificial streams is an efficient approach to generate multiple species effect values under quasi‐natural conditions that are relevant to natural streams.
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Common insecticide disrupts aquatic communities: A mesocosm-to-field ecological risk assessment of fipronil and its degradates in U.S. streams.

TL;DR: It is shown that a common insecticide frequently detected in U.S. streams is more toxic than previously thought and degrade stream communities in multiple regions of the United States.
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Benthic algal (periphyton) growth rates in response to nitrogen and phosphorus: Parameter estimation for water quality models.

TL;DR: These saturation concentrations provide an upper limit for streams where diatom growth can be expected to respond to nutrient levels and a benchmark for reducing nutrient concentrations to a point where benthic algal growth will be limited.
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Understanding the captivity effect on invertebrate communities transplanted into an experimental stream laboratory.

TL;DR: An experimental stream testing approach can support diverse larval macroinvertebrate communities for durations consistent with some chronic criterion development and life cycle assessments, indicating that mesocosm results are reasonably representative of real river insect communities.
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Uranium Bioaccumulation Dynamics in the Mayfly Neocloeon triangulifer and Application to Site-Specific Prediction.

TL;DR: U accumulation was limited in these wild populations due to a combination of factors including low concentrations of bioavailable dissolved U species, slow U uptake rates from food, and fast U elimination.