Diversity in the influence of temperature on the growth rates of freshwater algae, and its ecological relevance

By C. Butterwick, S. Heaney, J. Talling. 2004

367 citations recorded by the source corpus.

Subfields: Environmental Chemistry, Oceanography, Renewable Energy, Sustainability and the Environment

View Paper: https://www.semanticscholar.org/paper/2c29d33e69ee0f2ff428c837cb5017c55d66cb4d

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In Environmental Chemistry

In Oceanography

In Renewable Energy, Sustainability and the Environment

Citations in the corpus

Temperature effect on microalgae: a crucial factor for outdoor production (2013, background): “1 Temperature effect on microalgae growth rates (Butterwick et al. 2005; Kudo et al. 2000; Xin et al. 2011; Dermoun and Chaumont 1992) Rev Environ Sci Biotechnol (2013) 12:153–164 155”
Harmful Cyanobacterial Blooms: Causes, Consequences, and Controls (2013, background): “Warmer temperatures favor surface bloom-forming cyanobacterial genera because they are adapted to hot conditions and their maximal growth rates occur at relatively high temperatures; often in excess of 25 °C [12, 40, 120, 122].”
Linking traits to species diversity and community structure in phytoplankton (2010, background): “These include Aulacoseira (Foy & Gibson, 1993), Asterionella (Butterwick et al., 2005), and Rhizosolenia (Ignatiades & Smayda, 1970).”
Efficacy of microalgae for industrial wastewater treatment: a review on operating conditions, treatment efficiency and biomass productivity (2016, background): “…optimum value of temperature for the culture medium lies between 20 and 30 C. Microalgae can tolerate the temperature range of 16–27 C and the temperature lower than 16 C slow down the growth whereas higher than 35 C is harmful for the number of species (Butterwick et al. 2005; Teoh et al. 2005).”
Climate change: links to global expansion of harmful cyanobacteria. (2012, background): “Warming can selectively promote cyanobacterial growth because as prokaryotes, their growth rates are optimized at relatively high temperatures (Robarts and Zohary, 1987; Butterwick et al., 2005; Watkinson et al., 2005).”
Summer heatwaves promote blooms of harmful cyanobacteria (2008, methodology): “Parameter estimates are based on detailed measurements of physical structure and phytoplankton physiological data (Reynolds, 1997; Huisman et al., 2004; Robson & Hamilton, 2004; Butterwick et al., 2005), and the model predictions show good correspondence with the available data (Figs 2 and 3).”
Controlling harmful cyanobacterial blooms in a world experiencing anthropogenic and climatic-induced change. (2011, neutral): “form=Asterionella formosa (Butterwick et al., 2005), T.”
Tolerance of benthic diatoms from temperate aquatic and terrestrial habitats to experimental desiccation and temperature stress (2010, background): “The temperatures 30uC and 40uC were chosen because the lethal temperature for most diatoms is situated between these two values (Suzuki & Takahashi 1995; Butterwick et al. 2005).”
Warming advances top-down control and reduces producer biomass in a freshwater plankton community (2017, background): “For instance, some species with lower growth optima responded negatively to warming (Butterwick et al. 2005), while others responded positively (van Donk and Kilham 1990).”
Chytrid infections and diatom spring blooms: paradoxical effects of climate warming on fungal epidemics in lakes (2011, background): “The development of disease in Asterionella following infection by either one of the chytrids is highly comparable (Canter, 1967, 1969), and as every infection kills the host cell, epidemics are a major factor determining host population dynamics (see Ibelings et al. (2004) for review).”
Climate change: a catalyst for global expansion of harmful cyanobacterial blooms. (2009, background): “, 1976), the diatom Asterionella formosa (Butterwick et al., 2005) and the cryptophyte Cryptomonas marssonii (Butterwick et al.”