Mixotrophic algae in three ice-covered lakes of the Pocono Mountains, U.S.A.

1992 ◽  
Vol 28 (2) ◽  
pp. 263-272 ◽  
Author(s):  
ULRIKE-G. BERNINGER ◽  
DAVID A. CARON ◽  
ROBERT W. SANDERS
2018 ◽  
Vol 9 ◽  
Author(s):  
Lauren Mullen ◽  
Kim Boerrigter ◽  
Nicholas Ferriero ◽  
Jeff Rosalsky ◽  
Abigail van Buren Barrett ◽  
...  

2017 ◽  
Vol 7 (1) ◽  
Author(s):  
P. Carrillo ◽  
J. M. Medina-Sánchez ◽  
M. Villar-Argaiz ◽  
F. J. Bullejos ◽  
C. Durán ◽  
...  

2016 ◽  
Vol 76 (3) ◽  
pp. 219-232 ◽  
Author(s):  
M Gerea ◽  
JF Saad ◽  
I Izaguirre ◽  
C Queimaliños ◽  
JM Gasol ◽  
...  

1993 ◽  
Vol 50 (2) ◽  
pp. 370-380 ◽  
Author(s):  
David F. Bird ◽  
Jacob Kalff

We measured bacterial growth rates by labelled thymidine incorporation, grazing loss rates with fluorescent latex particles, and bacterial cell size and abundance within narrow size-fractions of freshwater bacterioplankton. Contrary to the predictions of standard allometric relationships, the smallest bacteria showed the lowest incorporation rate per cell and per unit DNA content. Cells trapped by 1- and 5-μm filters grew the fastest and were responsible for 86% of detected thymidine biosynthesis. Grazing studies in six lakes showed that grazing pressure from flagellated protozoans and mixotrophic algae on large bacterial cells was probably 2–40 times more intense than that on the smallest cells. We suggest that reduced grazing pressure on the smallest bacteria allows them to dominate numerically, despite their slower growth.


2021 ◽  
Author(s):  
Csaba F Vad ◽  
Claudia Schneider ◽  
Robert Fischer ◽  
Martin J Kainz ◽  
Robert Ptacnik

1. The importance of mixotrophic algae as key bacterivores in microbial food webs is increasingly acknowledged, but their effects on consumers is less understood, with previous studies having revealed contrasting results. In freshwater, this may be related to fundamental differences in the nutritional quality of two major mixotrophic groups. While cryptophytes are generally considered as high-quality food for zooplankton, chrysophytes (golden algae) are often referred to be toxic. 2. Using four chrysophyte species, we performed a comparative study as an attempt to generalize their dietary quality by (1) revealing their stoichiometric and biochemical profiles, and (2) quantifying their dietary effects in feeding bioassays with Daphnia longispina. We compared the observed effects to a known high-quality reference food (Cryptomonas sp.) and a starvation control as a reference for potential toxicity. 3. We found dramatic differences in survival and growth of D. longispina depending on the chrysophyte species provided as food. Even within the same genus, dietary quality ranged from deleterious to high. As this was not reflected in differences in cellular stoichiometry and fatty acid profiles, we suggest that toxicity may be the underlying mechanism. 4. Our results suggest that the dietary effects of chrysophytes cannot be generalised. Besides, the fact that a species previously reported to be deleterious turned out to be a beneficial food source suggests that toxic effects may dynamically vary depending on environmental cues, mode of nutrition or the investigated strain. 5. To fully understand the nutritional value of mixotrophic algae in aquatic food webs, representatives of multiple taxa need to be tested under a range of environmental conditions. This is also needed for a better predictive capability of climate change effects, as it may not only promote the dominance of mixotrophic algae, but also induce functional changes related to their nutritional quality.


Energies ◽  
2021 ◽  
Vol 14 (21) ◽  
pp. 6992
Author(s):  
Makoto M. Watanabe ◽  
Andreas Isdepsky

Microalgae have attracted significant attention worldwide as one of the most promising feedstock fossil fuel alternatives. However, there are a few challenges for algal fuels to compete with fossil fuels that need to be addressed. Therefore, this study reviews the R&D status of microalgae-based polyculture and biocrude oil production, along with wastewater treatment. Mixotrophic algae are free to some extent from light restrictions using organic matter and have the ability to grow well even in deep water-depth cultivation. It is proposed that integrating the mixotrophic microalgae polyculture and wastewater treatment process is the most promising and harmonizing means to simultaneously increase capacities of microalgae biomass production and wastewater treatment with a low land footprint and high robustness to perturbations. A large amount of mixotrophic algae biomass is harvested, concentrated, and dewatered by combining highly efficient sedimentation through flocculation and energy efficient filtration, which reduce the carbon footprint for algae fuel production and coincide with the subsequent hydrothermal liquefaction (HTL) conversion. HTL products are obtained with a relatively low carbon footprint and separated into biocrude oil, solid, aqueous, and gas fractions. Algae biomass feedstock-based HTL conversion has a high biocrude oil yield and quality available for existing oil refineries; it also has a bioavailability of the recycled nitrogen and phosphorus from the aqueous phase of algae community HTL. The HTL biocrude oil represents higher sustainability than conventional liquid fuels and other biofuels for the combination of greenhouse gas (GHG) and energy return on investment (EROI). Deep water-depth polyculture of mixotrophic microalgae using sewage has a high potential to produce sustainable biocrude oil within the land area of existing sewage treatment plants in Japan to fulfill imported crude oil.


2021 ◽  
Author(s):  
Gregory Pope ◽  
Jennifer Callanan ◽  
Jason Darley ◽  
Michael Flood ◽  
Jeffrey Wear ◽  
...  

<p>The wood ash contribution to soils represents a unique and important part of soil organic carbon following fires.  Wood ash imparts chemical and physical changes to the soil, evident in elements other than carbon.  Our case studies are from recent wildfires and experimental burns in mixed hardwood forests in the Pocono Mountains of Pennsylvania, USA.  In these studies, we identified increases in most of the major elements and some minor elements in soils following forest fires, analyzed with ICP-MS. Elements such as Mn, Mg, Na, Ca, Na, K, Cu, and Ba, derive from an infusion of biomass ash, with variable contribution depending on, for instance, tree species. In the case of Ba and Cu, their presence is distinctly different from any mineral parent material contribution to the soil, and therefore unique signatures of fire contribution. Signature post-fire elements persist in some cases over one year following the fire, and are found in both topsoil horizons and into illuvial soil horizons.</p><p>In the course of these investigations, we also found a curious depletion of all rare earth elements (REEs) and certain trace elements from the soil following forest fires, and in adjacent stream and wetland sediments. The post-fire difference in REE concentration was statistically significant (p < 0.10, N=51) in all but Eu and U, with light REEs La, Ce and Pr showing the most significant decreases. Among other trace elements, Sc (which behaves similarly to REEs), V, Cr, Ga, and Rb also exhibited statistically significant decreases (though other elements Cu and Sr increase along with the ash input). The reasons for the depletions are unclear. Other authors report that REE dynamics in soils are poorly understood, but may be associated with phosphates, carbonates, and silicates in the soil. These are relatively enriched via post-fire biomass ash, yet the associated REEs are missing. It is unlikely that the elements would have preferentially translocated through and below the soil profile. Erosion is ruled out, otherwise the ash-associated major and trace elements would also be depleted. Two possible causes for post-fire REE loss are 1) volatilization from the soil during the fire, and 2) rapid uptake by post-fire succession plants, notably ferns, which are known to bioaccumulate REEs. Further research is warranted, following the ongoing post-fire vegetation recovery, and the dynamics of REEs within the soil profile.       </p>


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