Abstract:Meromictic lakes provide a physically stable environment in which proxies for potentially harmful cyanobacteria are exceptionally well-preserved in the sediments. In Sunfish Lake, a meromictic lake that has recently become the focus of citizen concern due to the apparent rise in cyanobacteria blooms, we used a multi-proxy paleolimnological approach pairing novel spectral (i.e., VNIRS) and molecular (i.e., qPCR) assessment tools to explore long-term cyanobacteria trends. We hypothesized that climate change over… Show more
“…In meromictic lakes on unmanaged landscapes (without human activity), the lack of intermixing of water layers inhibits the periodical recharge of nutrient-enriched deep water into the surface layer and may restrict deep cyanobacteria layer development . However, meromictic lakes, such as Sunfish Lake, situated on managed landscapes (with human activity) may experience larger external nutrient loads that keep the lake in a moderately enriched state, supporting deep cyanobacteria layer development . Lake mixing strongly influences nutrient concentrations and thermal stability, which dictates the duration and intensity of stratification. , The lack of deep water-column mixing in meromictic lakes may favor stable thermal characteristics, which would be beneficial for deep cyanobacteria aggregating at depth.…”
Section: Resultsmentioning
confidence: 99%
“…Sunfish Lake (43°28′25″N, 80°38′01″W) is situated in the township of Wilmot, adjacent to Waterloo, Ontario, Canada. A small surface area (about 19 ha) paired with an unusually steep shoreline creates a lake morphology that supports meromixis , (Figure ). A 1,000 m buffer surrounding the lake is dominated by farmland (54.6% area) followed by mixed deciduous forests (36.4% area) .…”
Section: Methodsmentioning
confidence: 99%
“…A small surface area (about 19 ha) paired with an unusually steep shoreline creates a lake morphology that supports meromixis , (Figure ). A 1,000 m buffer surrounding the lake is dominated by farmland (54.6% area) followed by mixed deciduous forests (36.4% area) . The shoreline is well developed, with high cottage development occurring around the 1970s .…”
Section: Methodsmentioning
confidence: 99%
“…21 The lake is mesotrophic (i.e., average total phosphorus during the open water season of about 10 μg L −1 ), narrow, and has two deep recesses. The northwestern facing recess reaches a maximum depth of 19.8 m, and the southeastern recess reaches a maximum depth of 16.0 m. 22 2.2. Lake Sampling and Processing.…”
Section: Methodsmentioning
confidence: 99%
“…Duthie and Carter previously encountered a deep cyanobacteria layer composed predominately of Planktothrix sp. (previously Oscillatoria sp.) in the late 1960s at Sunfish Lake. Further, the paleorecord suggests a contemporary increase in cyanobacteria abundance, specifically Planktothrix sp . The aims of this study are to (a) characterize the deep cyanobacteria layer in Sunfish Lake, (b) evaluate the presence of toxins associated with the deep cyanobacteria layer to establish potential health risks, and (c) isolate the dominant cyanobacteria species and characterize the toxin-producing potential of these species to establish toxin–producer relationships.…”
The risk of human exposure to cyanotoxins is partially influenced by the location of toxin-producing cyanobacteria in waterbodies. Cyanotoxin production can occur throughout the water column, with deep water production representing a potential public health concern, specifically for drinking water supplies. Deep cyanobacteria layers are often unreported, and it remains to be seen if lower incident rates reflect an uncommon phenomenon or a monitoring bias. Here, we examine Sunfish Lake, Ontario, Canada as a case study lake with a known deep cyanobacteria layer. Cyanotoxin and other bioactive metabolite screening revealed that the deep cyanobacteria layer was toxigenic [0.03 μg L −1 microcystins (max) and 2.5 μg L −1 anabaenopeptins (max)]. The deep layer was predominantly composed of Planktothrix isothrix (exhibiting a lower cyanotoxin cell quota), with Planktothrix rubescens (exhibiting a higher cyanotoxin cell quota) found at background levels. The co-occurrence of multiple toxigenic Planktothrix species underscores the importance of routine surveillance for prompt identification leading to early intervention. For instance, microcystin concentrations in Sunfish Lake are currently below national drinking water thresholds, but shifting environmental conditions (e.g., in response to climate change or nutrient modification) could fashionan environment favoring P. rubescens, creating a scenario of greater cyanotoxin production. Future work should monitor the entire water column to help build predictive capacities for identifying waterbodies at elevated risk of developing deep cyanobacteria layers to safeguard drinking water supplies.
“…In meromictic lakes on unmanaged landscapes (without human activity), the lack of intermixing of water layers inhibits the periodical recharge of nutrient-enriched deep water into the surface layer and may restrict deep cyanobacteria layer development . However, meromictic lakes, such as Sunfish Lake, situated on managed landscapes (with human activity) may experience larger external nutrient loads that keep the lake in a moderately enriched state, supporting deep cyanobacteria layer development . Lake mixing strongly influences nutrient concentrations and thermal stability, which dictates the duration and intensity of stratification. , The lack of deep water-column mixing in meromictic lakes may favor stable thermal characteristics, which would be beneficial for deep cyanobacteria aggregating at depth.…”
Section: Resultsmentioning
confidence: 99%
“…Sunfish Lake (43°28′25″N, 80°38′01″W) is situated in the township of Wilmot, adjacent to Waterloo, Ontario, Canada. A small surface area (about 19 ha) paired with an unusually steep shoreline creates a lake morphology that supports meromixis , (Figure ). A 1,000 m buffer surrounding the lake is dominated by farmland (54.6% area) followed by mixed deciduous forests (36.4% area) .…”
Section: Methodsmentioning
confidence: 99%
“…A small surface area (about 19 ha) paired with an unusually steep shoreline creates a lake morphology that supports meromixis , (Figure ). A 1,000 m buffer surrounding the lake is dominated by farmland (54.6% area) followed by mixed deciduous forests (36.4% area) . The shoreline is well developed, with high cottage development occurring around the 1970s .…”
Section: Methodsmentioning
confidence: 99%
“…21 The lake is mesotrophic (i.e., average total phosphorus during the open water season of about 10 μg L −1 ), narrow, and has two deep recesses. The northwestern facing recess reaches a maximum depth of 19.8 m, and the southeastern recess reaches a maximum depth of 16.0 m. 22 2.2. Lake Sampling and Processing.…”
Section: Methodsmentioning
confidence: 99%
“…Duthie and Carter previously encountered a deep cyanobacteria layer composed predominately of Planktothrix sp. (previously Oscillatoria sp.) in the late 1960s at Sunfish Lake. Further, the paleorecord suggests a contemporary increase in cyanobacteria abundance, specifically Planktothrix sp . The aims of this study are to (a) characterize the deep cyanobacteria layer in Sunfish Lake, (b) evaluate the presence of toxins associated with the deep cyanobacteria layer to establish potential health risks, and (c) isolate the dominant cyanobacteria species and characterize the toxin-producing potential of these species to establish toxin–producer relationships.…”
The risk of human exposure to cyanotoxins is partially influenced by the location of toxin-producing cyanobacteria in waterbodies. Cyanotoxin production can occur throughout the water column, with deep water production representing a potential public health concern, specifically for drinking water supplies. Deep cyanobacteria layers are often unreported, and it remains to be seen if lower incident rates reflect an uncommon phenomenon or a monitoring bias. Here, we examine Sunfish Lake, Ontario, Canada as a case study lake with a known deep cyanobacteria layer. Cyanotoxin and other bioactive metabolite screening revealed that the deep cyanobacteria layer was toxigenic [0.03 μg L −1 microcystins (max) and 2.5 μg L −1 anabaenopeptins (max)]. The deep layer was predominantly composed of Planktothrix isothrix (exhibiting a lower cyanotoxin cell quota), with Planktothrix rubescens (exhibiting a higher cyanotoxin cell quota) found at background levels. The co-occurrence of multiple toxigenic Planktothrix species underscores the importance of routine surveillance for prompt identification leading to early intervention. For instance, microcystin concentrations in Sunfish Lake are currently below national drinking water thresholds, but shifting environmental conditions (e.g., in response to climate change or nutrient modification) could fashionan environment favoring P. rubescens, creating a scenario of greater cyanotoxin production. Future work should monitor the entire water column to help build predictive capacities for identifying waterbodies at elevated risk of developing deep cyanobacteria layers to safeguard drinking water supplies.
The Anthropocene has driven a transformative era where human activities exert unprecedented influence on Earth's biosphere. Consequently, synanthropic organisms, adept at thriving in human‐modified environments, have emerged. While well studied in terrestrial ecosystems, the presence and ecological importance of synanthropic species in aquatic ecosystems, specifically among cyanobacteria, are less understood. Cyanobacteria blooms, notorious for their detrimental effects on ecosystems and human health, are increasing in frequency and intensity globally. In this perspective, we explore the evidence supporting this rise of cyanobacteria blooms, emphasizing the roles of human‐induced eutrophication and climate change on select cyanobacteria genera. Cyanobacteria are not a monolith, with certain genera showing an observable increase within anthropogenically modified environments. We propose the establishment of a new sub‐branch of phycology that explicitly investigates the ecology and physiology of synanthropic cyanobacteria. Understanding the intricate interactions between synanthropic species and human populations is imperative for managing human‐altered ecosystems and conserving freshwater resources, particularly in the face of increasing global water insecurity.Practitioner Points
The rise in cyanobacteria blooms is driven by a small subset of human‐adapted genera—synanthropic cyanobacteria.
Research is needed to characterize synanthropic cyanobacteria, which will aid in developing tailored management approaches.
A paradigm shift from domesticating to “rewilding” landscapes and modifying behaviors to facilitate cohabitation are solutions to reducing risks.
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