Nitrogen form, concentration, and micronutrient availability affect microcystin production in cyanobacterial blooms

•Manipulated nitrogen (N) form, N and micronutrient (MN) concentrations in Microcystis culture and community HAB bioassay.•Microcystis grown in high urea and MN conditions produced the most biomass and particulate N.•Highest microcystin-LR concentrations occurred in high nitrate and MN conditions.•N...

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Veröffentlicht in:Harmful algae 2021-03, Vol.103, p.102002-102002, Article 102002
Hauptverfasser: Wagner, Nicole D., Quach, Emily, Buscho, Seth, Ricciardelli, Ashley, Kannan, Anupama, Naung, Sandi Win, Phillip, Grace, Sheppard, Berkeley, Ferguson, Lauren, Allen, Ashley, Sharon, Christopher, Duke, Jacquelyn R., Taylor, Raegyn B., Austin, Bradley J., Stovall, Jasmine K., Haggard, Brian E., Chambliss, C. Kevin, Brooks, Bryan W., Scott, J. Thad
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Sprache:eng
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Zusammenfassung:•Manipulated nitrogen (N) form, N and micronutrient (MN) concentrations in Microcystis culture and community HAB bioassay.•Microcystis grown in high urea and MN conditions produced the most biomass and particulate N.•Highest microcystin-LR concentrations occurred in high nitrate and MN conditions.•N addition stimulated biomass and microcystin concentrations in the community HAB bioassay.•MN amendment increased microcystin-LA concentrations in the community HAB bioassay. Harmful algal blooms (HABs) are increasing in magnitude, frequency, and duration caused by anthropogenic factors such as eutrophication and altered climatic regimes. While the concentrations and ratios of nitrogen (N) and phosphorus are correlated with bloom biomass and cyanotoxin production, there is less known about how N forms and micronutrients (MN) interact to regulate HABs and cyanotoxin production. Here, we used two separate approaches to examine how N and MN supply affects cyanobacteria biomass and cyanotoxin production. First, we used a Microcystis laboratory culture to examine how N and MN concentration and N form affected the biomass, particulate N, and microcystin-LR concentration and cell quotas. Then, we monitored the N, iron, molybdenum, and total microcystin concentrations from a hypereutrophic reservoir. From this hypereutrophic reservoir, we performed a community HAB bioassay to examine how N and MN addition affected the biomass, particulate N, and microcystin concentration. Microcystis laboratory cultures grown in high urea and MN conditions produced more biomass, particulate N, and had similar C:N stoichiometry, but lower microcystin-LR concentrations and cell quotas when compared to high nitrate and MN conditions. Our community HAB bioassay revealed no interactions between N concentration and MN addition caused by non-limiting MN background concentrations. Biomass, particulate N, and microcystin concentration increased with N addition. The community HAB amended with MN resulted in greater microcystin-LA concentration compared to non-MN amended community HABs. Our results highlight the complexity of how abiotic variables control biomass and cyanotoxin production in both laboratory cultures of Microcystis and community HABs.
ISSN:1568-9883
1878-1470
DOI:10.1016/j.hal.2021.102002