Copper-Based Aquatic Algaecide Adsorption and Accumulation Kinetics: Influence of Exposure Concentration and Duration for Controlling the Cyanobacterium Lyngbya wollei

Filamentous mat-forming cyanobacteria are increasingly impairing uses of freshwater resources. To effectively manage, a better understanding of control measures is needed. Copper (Cu)-based algaecide formulations are often applied to reactively control nuisance cyanobacterial blooms. This laboratory research assessed typical field exposure scenarios for the ability of Cu to partition to, and accumulate in Lyngbya wollei. Exposure factors (Cu concentration × duration) of 4, 8, 16, 24, 32 h were tested across three aqueous Cu concentrations (1, 2, 4 ppm). Results indicated that internally accumulated copper correlated with control of L. wollei, independent of adsorbed copper. L. wollei control was determined by filament viability and chlorophyll a concentrations. Similar exposure factors elicited similar internalized copper levels and consequent responses of L. wollei. Ultimately, a “concentration-exposure-time” (CET) model was created to assist water resource managers in selecting an appropriate treatment regime for a specific in-water infestation. By assessing the exposure concentration and duration required to achieve the internal threshold of copper (i.e., critical burden) that elicits control, water management objectives can be achieved while simultaneously decreasing the environmental loading of copper and potential for non-target species risks.

[1]  C. Bernard,et al.  Health hazards for terrestrial vertebrates from toxic cyanobacteria in surface water ecosystems. , 2003, Veterinary research.

[2]  B. M. Johnson,et al.  Comparative responses of target and nontarget species to exposures of a copper-based algaecide , 2014 .

[3]  J. Stauber,et al.  Use and limitations of microbial bioassays for assessing copper bioavailability in the aquatic environment , 2000 .

[4]  W. Bishop,et al.  Responses of Lyngbya magnifica Gardner to an algaecide exposure in the laboratory and field. , 2011, Ecotoxicology and environmental safety.

[5]  W. T. Blevins,et al.  Geosmin-producing species of Streptomyces and Lyngbya from aquaculture ponds , 1993 .

[6]  A. E. Greenberg,et al.  Standard methods for the examination of water and wastewater : supplement to the sixteenth edition , 1988 .

[7]  J. Stauber,et al.  Mechanism of toxicity of ionic copper and copper complexes to algae , 1987 .

[8]  B. J. Speziale,et al.  LYNGBYA INFESTATIONS: COMPARATIVE TAXONOMY OF LYNGBYA WOLLEI COMB. NOV. (CYANOBACTERIA) 1 , 1992 .

[9]  M. Seve,et al.  Increasing occurrence of the benthic filamentous cyanobacterium Lyngbya wollei: a symptom of freshwater ecosystem degradation , 2014, Freshwater Science.

[10]  L. Sigg,et al.  Binding of Cu(II) to algae in a metal buffer , 1990 .

[11]  J. R. Martin,et al.  Interaction of metals and protons with Algae. 2. Ion exchange in adsorption and metal displacement by protons , 1990 .

[12]  F. Beolchini,et al.  Removal of metals by biosorption: a review , 1997 .

[13]  S. Daroub,et al.  Allelopathic Effects of Pistia stratiotes (Araceae) and Lyngbya wollei Farlow ex Gomont (Oscillariaceae) on Seed Germination and Root Growth , 2014 .

[14]  W. Bishop,et al.  Affinity and Efficacy of Copper Following an Algicide Exposure: Application of the Critical Burden Concept for Lyngbya wollei Control in Lay Lake, AL , 2015, Environmental Management.

[15]  Boqiang Qin,et al.  Mitigating cyanobacterial harmful algal blooms in aquatic ecosystems impacted by climate change and anthropogenic nutrients. , 2016, Harmful algae.

[16]  E. Phlips,et al.  Characterization of paralytic shellfish toxins from Lyngbya wollei dominated mats collected from two Florida springs , 2012 .

[17]  West Michael Bishop A Risk-based Decision Information System for Selecting an Algal Management Program. , 2016 .

[18]  M. Sadowsky,et al.  The establishment of the nuisance cyanobacteria Lyngbya wollei in Lake St. Clair and its potential to harbor fecal indicator bacteria , 2013 .

[19]  K. White,et al.  Copper adsorption kinetics of cultured algal cells and freshwater phytoplankton with emphasis on cell surface characteristics , 2005, Journal of Applied Phycology.

[20]  G. Shaw,et al.  First evidence for the production of cylindrospermopsin and deoxy-cylindrospermopsin by the freshwater benthic cyanobacterium, Lyngbya wollei (Farlow ex Gomont) Speziale and Dyck , 2007 .

[21]  J. Kadukova,et al.  Comparison of differences between copper bioaccumulation and biosorption. , 2005, Environment international.

[22]  G. Gorbi,et al.  Chromium toxicity on two linked trophic levels. II. Morphophysiological effects on Scenedesmus acutus. , 1993, Ecotoxicology and environmental safety.

[23]  J. Cairns,et al.  The scientific basis of bioassays , 1989, Hydrobiologia.

[24]  K. Knauer,et al.  ADSORPTION AND UPTAKE OF COPPER BY THE GREEN ALGA SCENEDESMUS SUBSPICATUS (CHLOROPHYTA) 1 , 1997 .

[25]  W. Bishop,et al.  Responses of Lyngbya wollei to Exposures of Copper-Based Algaecides: The Critical Burden Concept , 2012, Archives of Environmental Contamination and Toxicology.

[26]  B. Tripathi,et al.  Oxidative stress in Scenedesmus sp. during short- and long-term exposure to Cu2+ and Zn2+. , 2006, Chemosphere.

[27]  P. Dassow,et al.  The strain concept in phytoplankton ecology , 2009 .

[28]  Hai Yan,et al.  Toxicity and bioaccumulation of copper in three green microalgal species. , 2002, Chemosphere.

[29]  W. Carmichael,et al.  Human Fatalities from Cyanobacteria: Chemical and Biological Evidence for Cyanotoxins , 2001 .

[30]  L. Sigg,et al.  Chemical and Spectroscopic Characterization of Algae Surfaces , 1997 .

[31]  W. Sunda,et al.  Processes regulating cellular metal accumulation and physiological effects : Phytoplankton as model systems , 1998 .

[32]  M. Twiss,et al.  Laboratory selection for copper tolerance in Scenedesmus acutus (Chlorophyceae) , 1993 .