Upstream nitrogen availability determines the Microcystis salt tolerance and influences microcystins release in brackish water
Copyright © 2024. Published by Elsevier Ltd..
The occurrence of large Microcystis biomass in brackish waters is primarily caused by its downward transportation from the upstream freshwater lakes and reservoirs through rivers rather than due to in situ bloom formation. Factors that determine the survival of freshwater cyanobacteria in brackish waters have not been well investigated. Here, we studied the spatiotemporal variability of inorganic nitrogen in an upstream lake and conducted laboratory and in-situ experiments to assess the role of nitrogen availability on the salt tolerance of Microcystis and the release of microcystins. A series of field experiments were carried out during bloom seasons to evaluate the salt tolerance of natural Microcystis colonies. The salt tolerance threshold varied from 7 to 17 and showed a positive relationship with intracellular carbohydrate content and a negative relationship with nitrogen availability in water. In August when upstream nitrogen availability was lower, the Microcystis colonies could maintain their biomass even after a sudden increase in salinity from 4 to 10. Laboratory-cultivated Microcystis that accumulated higher carbohydrate content at lower nitrogen availability showed better cell survival at higher salinity. The sharp release of microcystins into the surrounding water occurred when salinity exceeded the salt tolerance threshold of the Microcystis. Thus, Microcystis with higher salt tolerance can accumulate more toxins in cells. The obtained results suggest that the cell survival and toxin concentration in brackish waters depend on the physiological properties of Microcystis formed in the upstream waters. Thus, the life history of Microcystis in upstream waters could have a significant impact on its salt tolerance in downstream brackish waters, where the ecological risk of the salt-tolerant Microcystis requires special and careful management in summer at low nitrogen availability.
| Medienart: |
E-Artikel |
|---|
| Erscheinungsjahr: |
2024 |
|---|---|
| Erschienen: |
2024 |
| Enthalten in: |
Zur Gesamtaufnahme - volume:252 |
|---|---|
| Enthalten in: |
Water research - 252(2024) vom: 15. Feb., Seite 121213 |
| Sprache: |
Englisch |
|---|
| Beteiligte Personen: |
Li, Xinlu [VerfasserIn] |
|---|
| Links: |
|---|
| Themen: |
059QF0KO0R |
|---|
| Anmerkungen: |
Date Completed 29.02.2024 Date Revised 29.02.2024 published: Print-Electronic Citation Status MEDLINE |
|---|
| doi: |
10.1016/j.watres.2024.121213 |
|---|
| funding: |
|
|---|---|
| Förderinstitution / Projekttitel: |
|
| PPN (Katalog-ID): |
NLM367961318 |
|---|
| LEADER | 01000caa a22002652 4500 | ||
|---|---|---|---|
| 001 | NLM367961318 | ||
| 003 | DE-627 | ||
| 005 | 20240229234925.0 | ||
| 007 | cr uuu---uuuuu | ||
| 008 | 240203s2024 xx |||||o 00| ||eng c | ||
| 024 | 7 | |a 10.1016/j.watres.2024.121213 |2 doi | |
| 028 | 5 | 2 | |a pubmed24n1311.xml |
| 035 | |a (DE-627)NLM367961318 | ||
| 035 | |a (NLM)38306752 | ||
| 035 | |a (PII)S0043-1354(24)00113-1 | ||
| 040 | |a DE-627 |b ger |c DE-627 |e rakwb | ||
| 041 | |a eng | ||
| 100 | 1 | |a Li, Xinlu |e verfasserin |4 aut | |
| 245 | 1 | 0 | |a Upstream nitrogen availability determines the Microcystis salt tolerance and influences microcystins release in brackish water |
| 264 | 1 | |c 2024 | |
| 336 | |a Text |b txt |2 rdacontent | ||
| 337 | |a ƒaComputermedien |b c |2 rdamedia | ||
| 338 | |a ƒa Online-Ressource |b cr |2 rdacarrier | ||
| 500 | |a Date Completed 29.02.2024 | ||
| 500 | |a Date Revised 29.02.2024 | ||
| 500 | |a published: Print-Electronic | ||
| 500 | |a Citation Status MEDLINE | ||
| 520 | |a Copyright © 2024. Published by Elsevier Ltd. | ||
| 520 | |a The occurrence of large Microcystis biomass in brackish waters is primarily caused by its downward transportation from the upstream freshwater lakes and reservoirs through rivers rather than due to in situ bloom formation. Factors that determine the survival of freshwater cyanobacteria in brackish waters have not been well investigated. Here, we studied the spatiotemporal variability of inorganic nitrogen in an upstream lake and conducted laboratory and in-situ experiments to assess the role of nitrogen availability on the salt tolerance of Microcystis and the release of microcystins. A series of field experiments were carried out during bloom seasons to evaluate the salt tolerance of natural Microcystis colonies. The salt tolerance threshold varied from 7 to 17 and showed a positive relationship with intracellular carbohydrate content and a negative relationship with nitrogen availability in water. In August when upstream nitrogen availability was lower, the Microcystis colonies could maintain their biomass even after a sudden increase in salinity from 4 to 10. Laboratory-cultivated Microcystis that accumulated higher carbohydrate content at lower nitrogen availability showed better cell survival at higher salinity. The sharp release of microcystins into the surrounding water occurred when salinity exceeded the salt tolerance threshold of the Microcystis. Thus, Microcystis with higher salt tolerance can accumulate more toxins in cells. The obtained results suggest that the cell survival and toxin concentration in brackish waters depend on the physiological properties of Microcystis formed in the upstream waters. Thus, the life history of Microcystis in upstream waters could have a significant impact on its salt tolerance in downstream brackish waters, where the ecological risk of the salt-tolerant Microcystis requires special and careful management in summer at low nitrogen availability | ||
| 650 | 4 | |a Journal Article | |
| 650 | 4 | |a Brackish water | |
| 650 | 4 | |a Microcystis blooms | |
| 650 | 4 | |a Nitrogen availability | |
| 650 | 4 | |a Salt tolerance | |
| 650 | 7 | |a Microcystins |2 NLM | |
| 650 | 7 | |a Nitrogen |2 NLM | |
| 650 | 7 | |a N762921K75 |2 NLM | |
| 650 | 7 | |a Water |2 NLM | |
| 650 | 7 | |a 059QF0KO0R |2 NLM | |
| 650 | 7 | |a Carbohydrates |2 NLM | |
| 700 | 1 | |a Li, Lei |e verfasserin |4 aut | |
| 700 | 1 | |a Huang, Yingying |e verfasserin |4 aut | |
| 700 | 1 | |a Wu, Haipeng |e verfasserin |4 aut | |
| 700 | 1 | |a Sheng, Shiwen |e verfasserin |4 aut | |
| 700 | 1 | |a Jiang, Xinran |e verfasserin |4 aut | |
| 700 | 1 | |a Chen, Xuechu |e verfasserin |4 aut | |
| 700 | 1 | |a Ostrovsky, Ilia |e verfasserin |4 aut | |
| 773 | 0 | 8 | |i Enthalten in |t Water research |d 1990 |g 252(2024) vom: 15. Feb., Seite 121213 |w (DE-627)NLM111404762 |x 1879-2448 |7 nnns |
| 773 | 1 | 8 | |g volume:252 |g year:2024 |g day:15 |g month:02 |g pages:121213 |
| 856 | 4 | 0 | |u http://dx.doi.org/10.1016/j.watres.2024.121213 |3 Volltext |
| 912 | |a GBV_USEFLAG_A | ||
| 912 | |a GBV_NLM | ||
| 951 | |a AR | ||
| 952 | |d 252 |j 2024 |b 15 |c 02 |h 121213 | ||