4.7 Article

Occurrence of BMAA Isomers in Bloom-Impacted Lakes and Reservoirs of Brazil, Canada, France, Mexico, and the United Kingdom

Journal

TOXINS
Volume 14, Issue 4, Pages -

Publisher

MDPI
DOI: 10.3390/toxins14040251

Keywords

lake water; beta-N-methyl-amino-1-alanine (BMAA); 2,4-diaminobutyric acid (DAB); N-(2-aminoethyl) glycine (AEG); trichloroacetic acid (TCA); temporal trends

Funding

  1. Genome Canada
  2. Genome Quebec (LSARP 2016)
  3. Natural Sciences and Engineering Research Council of Canada (NSERC-CRSNG) [STPGP 478774]
  4. Quebec Research Fund (FRQ) [PR183278]
  5. Canada Foundation for Innovation (CFI) [30044]
  6. GlobalWater Futures project FORMBLOOM (Canada First Research Excellence Fund)
  7. Furnas Centais Eletricas SA (FURNAS), Companhia Eletrica de Minas Gerais (CEMIG)
  8. Fundacao de Amparo a Pesquisa de Minas Gerais (FAPEMIG)
  9. National Council of Science and Technology (CONACYT) Mexico
  10. ANSWER project (France) [ANR-16-CE320009-02]

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This study evaluated the impact of trichloroacetic acid on the detection of BMAA isomers in lake water samples and found that its addition significantly increased detection rates and levels. Additionally, an investigation of lakes from multiple countries revealed a higher occurrence of AEG and DAB isomers compared to BAMA and BMAA.
The neurotoxic alkaloid beta-N-methyl-amino-1-alanine (BMAA) and related isomers, including N-(2-aminoethyl glycine) (AEG), beta-amino-N-methyl alanine (BAMA), and 2,4-diaminobutyric acid (DAB), have been reported previously in cyanobacterial samples. However, there are conflicting reports regarding their occurrence in surface waters. In this study, we evaluated the impact of amending lake water samples with trichloroacetic acid (0.1 M TCA) on the detection of BMAA isomers, compared with pre-existing protocols. A sensitive instrumental method was enlisted for the survey, with limits of detection in the range of 5-10 ng L-1. Higher detection rates and significantly greater levels (paired Wilcoxon's signed-rank tests, p < 0.001) of BMAA isomers were observed in TCA-amended samples (method B) compared to samples without TCA (method A). The overall range of B/A ratios was 0.67-8.25 for AEG (up to +725%) and 0.69-15.5 for DAB (up to +1450%), with absolute concentration increases in TCA-amended samples of up to +15,000 ng L-1 for AEG and +650 ng L-1 for DAB. We also documented the trends in the occurrence of BMAA isomers for a large breadth of field-collected lakes from Brazil, Canada, France, Mexico, and the United Kingdom. Data gathered during this overarching campaign (overall, n = 390 within 45 lake sampling sites) indicated frequent detections of AEG and DAB isomers, with detection rates of 30% and 43% and maximum levels of 19,000 ng L-1 and 1100 ng L-1, respectively. In contrast, BAMA was found in less than 8% of the water samples, and BMAA was not found in any sample. These results support the analyses of free-living cyanobacteria, wherein BMAA was often reported at concentrations of 2-4 orders of magnitude lower than AEG and DAB. Seasonal measurements conducted at two bloom-impacted lakes indicated limited correlations of BMAA isomers with total microcystins or chlorophyll-a, which deserves further investigation.

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