No evidence of an allelopathic effect of Eurasian watermilfoil (Myriophyllum spicatum) on cyanobacteria in natural lakes
Data files
Nov 16, 2025 version files 86.49 KB
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Bergeron_Data.csv
76.24 KB
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README.md
10.25 KB
Abstract
Eurasian watermilfoil (Myriophyllum spicatum) is an exotic vascular plant in North America and highly invasive in lacustrine environments. This plant forms dense, extensive beds that can interfere with recreational activities. High concentrations of Eurasian watermilfoil have been shown in laboratory experiments to cause mortality or low growth rates to several species of cyanobacteria, because of allelopathic molecules (fatty acids, polyphenols) released into the water by the plant. The main objective of this study was to verify whether a causal link between Eurasian watermilfoil and cyanobacteria could be established in two infested lakes of southern Québec, Canada. Some fatty acids or polyphenols (ellagic, nonanoic, octadecenoic, and oleic acids) were detected in summer and autumn in the water, but in concentrations well below (30 to 35 000 times lower) the theoretical concentrations at which they reduce the growth of cyanobacteria. There was no evidence of allelopathic effects of Eurasian watermilfoil on the cyanobacterial assemblages. However, some cyanobacterial species known to be influenced by Eurasian watermilfoil, in particular Microcystis aeruginosa, were not specifically identified in this study, so caution must be exercised before concluding that there is no allelopathic effect.
Dataset DOI: 10.5061/dryad.fn2z34v6f
Description of the data and file structure
These data were collected as part of a field study investigating whether the invasive aquatic plant Eurasian watermilfoil (Myriophyllum spicatum) exerts allelopathic effects on cyanobacterial assemblages in natural lake systems. The dataset includes:
- Quantification of specific allelochemicals (fatty acids and polyphenols) in water samples
- Cyanobacterial cell abundance and assemblage data (to genus level) from water samples collected at sites with and without M. spicatum beds;
- Associated physicochemical parameters (e.g., total nitrogen, total phosphorus, nitrite–nitrate, water temperature, dissolved oxygen) from the same sampling locations and periods.
Files and variables
Bergeron_Data.csv
METADATA:
Name (Unit): Description
Date: Date of the sampling
Outing: Field outing number
Lake: Name of the lake
Replicate: Replicate
Site: Name of the site
Sample number: Number of the sample
Id: Id of the sample
Precipitation: Qualitative description of precipitation conditions prior to the sampling event.
Sky condition: Visual observation of sky conditions at the time of sampling.
Wave type: Visual assessment of surface water conditions based on wave activity during sampling.
Wind direction: Cardinal direction from which the wind is blowing at the time of sampling.
Water level (m): Water level at the lake outlet, at the Cyrille-Delage dam
Precipitation (mm): Daily precipitation on the sampling day.
Cumulative precipitation (mm): Total cumulative precipitation since January 1st
Cumulative degree-days (°C): Cumulative degree-days (above 0°C) since January 1st
Start time: Sampling start time.
End time: Sampling end time.
Average wind speed (m/s): Average wind speed at sampling site
Maximum wind speed (m/s): Maximum wind speed at sampling site
Maximum depth (m): Maximum depth at sampling site
Atmospheric pressure (mmHg): Atmospheric pressure at sampling site
Air temperature (°C): Air temperature at sampling site
Water transparency (m): Water transparency at sampling site
0 m Water temperature (°C): Water temperature at the surface
0 m pH: pH at the surface
0 m ORP (mV): Redox potential at the surface
0 m Conductivity (ms/cm): Conductivity at the surface
0 m Dissolved oxygen (%): Dissolved oxygen percentage at the surface
1 m Water temperature (°C): Water temperature at a depth of one meter
1 m pH: pH at a depth of one meter
1 m ORP (mV): Redox potential at a depth of one meter
1 m Conductivity (ms/cm): Conductivity at a depth of one meter
1 m Dissolved oxygen (%): Dissolved oxygen percentage at a depth of one meter
2 m Water temperature (°C): Water temperature at a depth of two meters
2 m pH: pH at a depth of two meters
2 m ORP (mV): Redox potential at a depth of two meters
2 m Conductivity (ms/cm): Conductivity at a depth of two meters
2 m Dissolved oxygen (%): Dissolved oxygen percentage at a depth of two meters
3 m Water temperature (°C): Water temperature at a depth of three meters
3 m pH: pH at a depth of three meters
3 m ORP (mV): Redox potential at a depth of three meters
3 m Conductivity (ms/cm): Conductivity at a depth of three meters
3 m Dissolved oxygen (%): Dissolved oxygen percentage at a depth of three meters
Ammoniacal nitrogen (µg N/l): Concentration of ammoniacal nitrogen in the water column
Nitrites and nitrates (mg N/l): Concentration of nitrites and nitrates in the water column
Total phosphorus (µg P/l): Concentration of total phosphorus in the water column
Total nitrogen (mg N/l): Concentration of total nitrogen in the water column
Dissolved orthophosphates (µg P/l): Concentration of dissolved orthophosphates in the water column; NULL means no dissolved orthophosphates were detected
Nonanoic acid (µg/l): Concentration of nonanoic acid in the water column LOD:Limite of detection
Oleic acid (µg/l): Concentration of oleic acid in the water column LOQ: Limit of Quantification
Octadecenoic acid (µg/l): Concentration of octadecenoic acid in the water column
Gallic acid (µg/l): Concentration of gallic acid in the water column
Pyrogallol (µg/l): Concentration of pyrogallol in the water column
Catechine (µg/l): Concentration of catechine in the water column
Eugeniine (µg/l): Concentration of eugeniine in the water column
Ellagic acid (µg/l): Concentration of ellagic acid in the water column
Cyanobacteria (cell/ml): Concentration of cyanobacteria in the water column
Anabeanopsis (cell/ml): Concentration of Anabeanopsis in the water column
Aphanizomenon sp. (cell/ml): Concentration of Aphanizomenon sp in the water column
Aphanocapsa sp. (cell/ml): Concentration of Aphanocapsa sp in the water column
Aphanothece sp. (cell/ml): Concentration of Aphanothece sp in the water column
Borzia sp. (cell/ml): Concentration of Borzia sp in the water column
Chroococcus sp. (cell/ml): Concentration of Chroococcus sp in the water column
Coelomoron sp. (cell/ml): Concentration of Coelomoron sp in the water column
Coelosphaerium sp. (cell/ml): Concentration of Coelosphaerium sp in the water column
Cuspidothrix sp. (cell/ml): Concentration of Cuspidothrix sp in the water column
Cyanodictyon sp. (cell/ml): Concentration of Cyanodictyon sp in the water column
Cyanogranis sp. (cell/ml): Concentration of Cyanogranis sp in the water column
Cylindrospermopsis sp. (cell/ml): Concentration of Cylindrospermopsis sp in the water column
Cylindrospermum sp. (cell/ml): Concentration of Cylindrospermum sp in the water column
Dolichospermum sp. (Anabena sp.) (cell/ml): Concentration of Dolichospermum sp Anabena sp in the water column
Eucapsis sp. (cell/ml): Concentration of Eucapsis sp in the water column
Geitlerinema sp. (cell/ml): Concentration of Geitlerinema sp in the water column
Gloeocapsa sp. (cell/ml): Concentration of Gloeocapsa sp in the water column
Gomphospheria sp. (cell/ml): Concentration of Gomphospheria sp in the water column
Jaaginema sp. (cell/ml): Concentration of Jaaginema sp in the water column
Komvophoron sp. (cell/ml): Concentration of Komvophoron sp in the water column
Lemmermaniella sp. (cell/ml): Concentration of Lemmermaniella sp in the water column
Leptolyngbya sp. (cell/ml): Concentration of Leptolyngbya sp in the water column
Limnothrix sp. (cell/ml): Concentration of Limnothrix sp in the water column
Lyngbya sp. (cell/ml): Concentration of Lyngbya sp in the water column
Merismopedia sp. (cell/ml): Concentration of Merismopedia sp in the water column
Microcystis sp. (cell/ml): Concentration of Microcystis sp in the water column
Oscillatoria sp. (cell/ml): Concentration of Oscillatoria sp in the water column
Phormidium sp. (cell/ml): Concentration of Phormidium sp in the water column
Planktolyngbya sp. (cell/ml): Concentration of Planktolyngbya sp in the water column
Planktothrix sp. (cell/ml): Concentration of Planktothrix sp in the water column
Pseudanabaena sp. (cell/ml): Concentration of Pseudanabaena sp in the water column
Rhabdoderma sp. (cell/ml): Concentration of Rhabdoderma sp in the water column
Rhabdogloea sp. (Dactylococcopsis sp.) (cell/ml): Concentration of Rhabdogloea sp in the water column
Radiocystis sp. (cell/ml): Concentration of Radiocystis sp in the water column
Raphidiopsis sp. (cell/ml): Concentration of Raphidiopsis sp in the water column
Snowella sp. (cell/ml): Concentration of Snowella sp in the water column
Spirulina sp. (cell/ml): Concentration of Spirulina sp in the water column
Synechococcus sp. (cell/ml): Concentration of Synechococcus sp in the water column
Synechocystis sp. (cell/ml): Concentration of Synechocystis sp in the water column
Woronichinia sp. (cell/ml): Concentration of Woronichinia sp in the water column
Other blue-green algae (cell/ml): Concentration of other blue-green algae in the water column
Code/software
Data analyses were conducted using two main software environments:
- Stata version 16.0 (StataCorp, 2019)
- Used for the multiple regression and panel data analyses.
- Included procedures for random effects models with spatial fixed effects, Breusch–Pagan and Pesaran tests for cross-sectional dependence, heteroscedasticity testing (Breusch–Pagan), normality testing of residuals (Shapiro–Wilk and histogram inspection), and multicollinearity assessment using the Variance Inflation Factor (VIF).
- Based on the VIF results, two variables (cumulative degree-days and air temperature) were removed from the final model.
- R version 2023.06.2 (The R Project for Statistical Computing, 2023)
- Used for the analysis of variance (two-way ANOVA, model 1) to compare cyanobacterial concentrations between sampling dates and sites with vs. without Myriophyllum spicatum.
- Implemented functions:
aov()for ANOVAshapiro.test()for residual normality (Shapiro–Wilk test)leveneTest()(from the car package) for homogeneity of variances.
- A canonical correspondence analysis (CCA) was also performed using the function
cca()from the vegan package (version 2.6-4; Oksanen et al., 2022) to explore relationships between cyanobacterial assemblages and environmental variables.
All analyses used freely available or licensed software as noted above. No custom scripts were developed; only standard functions and statistical packages were used.
Access information
Other publicly accessible locations of the data:
- Gouvernement du Québec. (2023b). Niveau d’eau et débit. Ministère de l’Environnement, de la Lutte contre les changements climatiques, de la Faune et des Parcs du Québec. https://www.cehq.gouv.qc.ca/hydrometrie/
- Environnement Canada. (2023). Données historiques. Gouvernement du Canada. https://climat.meteo.gc.ca/historical_data/search_historic_data_f.html
