Effects of Phenolic Pollution on Interspecific Competition between Microcystis aeruginosa and Chlorella pyrenoidosa and their Photosynthetic Responses
The demand for phenolic compounds has been increasing rapidly, which has intensified the production and usage of phenol at a commercial scale. In some polluted water bodies, phenol has become one of the typical aromatic contaminants. Such water bodies are inescapably influenced by nutrients from hum...
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Published in | International journal of environmental research and public health Vol. 16; no. 20; p. 3947 |
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Abstract | The demand for phenolic compounds has been increasing rapidly, which has intensified the production and usage of phenol at a commercial scale. In some polluted water bodies, phenol has become one of the typical aromatic contaminants. Such water bodies are inescapably influenced by nutrients from human activities, and also suffer from nuisance cyanobacterial blooms. While phenolic pollution threatens water safety and ecological balance, algal cells are ubiquitous and sensitive to pollutants. Therefore, effects of phenolic pollution on interspecific competition between a bloom-forming cyanobacterium and other common alga merit quantitative investigation. In this study, the effects of phenol on Microcystis aeruginosa (M. aeruginosa, a bloom-forming cyanobacterium) and Chlorella pyrenoidosa (C. pyrenoidosa, a ubiquitous green alga) were analyzed in mono- and co-cultures. The two species were exposed to a series of phenol treatments (0, 2, 20, and 200 μg mL−1). Population dynamics were measured by a flow cytometer and analyzed by the Lotka-Volterra model. The results showed that M. aeruginosa was more sensitive to phenol (EC50 = 80.8 ± 0.16 μg mL−1) compared to C. pyrenoidosa (EC50 = 631.4 ± 0.41 μg mL−1) in mono-cultures. M. aeruginosa won in the co-cultures when phenol was below or equal to 20 μg mL−1, while C. pyrenoidosa became the dominant species in the 200 μg mL−1 treatment. Photosynthetic activity was measured by a fluometer. Results showed phenol significantly impacted the photosynthetic activity of M. aeruginosa by inhibiting the acceptor side of its photosystem II (PSII), while such inhibition in C. pyrenoidosa was only observed in the highest phenol treatment (200 μg mL−1). This study provides a better understanding for predicting the succession of algal community structure in water bodies susceptible to phenolic contamination. Moreover, it reveals the mechanism on photosynthetic responses of these two species under phenolic stress. |
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AbstractList | The demand for phenolic compounds has been increasing rapidly, which has intensified the production and usage of phenol at a commercial scale. In some polluted water bodies, phenol has become one of the typical aromatic contaminants. Such water bodies are inescapably influenced by nutrients from human activities, and also suffer from nuisance cyanobacterial blooms. While phenolic pollution threatens water safety and ecological balance, algal cells are ubiquitous and sensitive to pollutants. Therefore, effects of phenolic pollution on interspecific competition between a bloom-forming cyanobacterium and other common alga merit quantitative investigation. In this study, the effects of phenol on
Microcystis aeruginosa
(
M. aeruginosa
, a bloom-forming cyanobacterium) and
Chlorella pyrenoidosa
(
C. pyrenoidosa
, a ubiquitous green alga) were analyzed in mono- and co-cultures. The two species were exposed to a series of phenol treatments (0, 2, 20, and 200 μg mL
−1
). Population dynamics were measured by a flow cytometer and analyzed by the Lotka-Volterra model. The results showed that
M. aeruginosa
was more sensitive to phenol (EC
50
= 80.8 ± 0.16 μg mL
−1
) compared to
C. pyrenoidosa
(EC
50
= 631.4 ± 0.41 μg mL
−1
) in mono-cultures.
M. aeruginosa
won in the co-cultures when phenol was below or equal to 20 μg mL
−1
, while
C. pyrenoidosa
became the dominant species in the 200 μg mL
−1
treatment. Photosynthetic activity was measured by a fluometer. Results showed phenol significantly impacted the photosynthetic activity of
M. aeruginosa
by inhibiting the acceptor side of its photosystem II (PSII), while such inhibition in
C. pyrenoidosa
was only observed in the highest phenol treatment (200 μg mL
−1
). This study provides a better understanding for predicting the succession of algal community structure in water bodies susceptible to phenolic contamination. Moreover, it reveals the mechanism on photosynthetic responses of these two species under phenolic stress. The demand for phenolic compounds has been increasing rapidly, which has intensified the production and usage of phenol at a commercial scale. In some polluted water bodies, phenol has become one of the typical aromatic contaminants. Such water bodies are inescapably influenced by nutrients from human activities, and also suffer from nuisance cyanobacterial blooms. While phenolic pollution threatens water safety and ecological balance, algal cells are ubiquitous and sensitive to pollutants. Therefore, effects of phenolic pollution on interspecific competition between a bloom-forming cyanobacterium and other common alga merit quantitative investigation. In this study, the effects of phenol on Microcystis aeruginosa (M. aeruginosa, a bloom-forming cyanobacterium) and Chlorella pyrenoidosa (C. pyrenoidosa, a ubiquitous green alga) were analyzed in mono- and co-cultures. The two species were exposed to a series of phenol treatments (0, 2, 20, and 200 μg mL-1). Population dynamics were measured by a flow cytometer and analyzed by the Lotka-Volterra model. The results showed that M. aeruginosa was more sensitive to phenol (EC50 = 80.8 ± 0.16 μg mL-1) compared to C. pyrenoidosa (EC50 = 631.4 ± 0.41 μg mL-1) in mono-cultures. M. aeruginosa won in the co-cultures when phenol was below or equal to 20 μg mL-1, while C. pyrenoidosa became the dominant species in the 200 μg mL-1 treatment. Photosynthetic activity was measured by a fluometer. Results showed phenol significantly impacted the photosynthetic activity of M. aeruginosa by inhibiting the acceptor side of its photosystem II (PSII), while such inhibition in C. pyrenoidosa was only observed in the highest phenol treatment (200 μg mL-1). This study provides a better understanding for predicting the succession of algal community structure in water bodies susceptible to phenolic contamination. Moreover, it reveals the mechanism on photosynthetic responses of these two species under phenolic stress.The demand for phenolic compounds has been increasing rapidly, which has intensified the production and usage of phenol at a commercial scale. In some polluted water bodies, phenol has become one of the typical aromatic contaminants. Such water bodies are inescapably influenced by nutrients from human activities, and also suffer from nuisance cyanobacterial blooms. While phenolic pollution threatens water safety and ecological balance, algal cells are ubiquitous and sensitive to pollutants. Therefore, effects of phenolic pollution on interspecific competition between a bloom-forming cyanobacterium and other common alga merit quantitative investigation. In this study, the effects of phenol on Microcystis aeruginosa (M. aeruginosa, a bloom-forming cyanobacterium) and Chlorella pyrenoidosa (C. pyrenoidosa, a ubiquitous green alga) were analyzed in mono- and co-cultures. The two species were exposed to a series of phenol treatments (0, 2, 20, and 200 μg mL-1). Population dynamics were measured by a flow cytometer and analyzed by the Lotka-Volterra model. The results showed that M. aeruginosa was more sensitive to phenol (EC50 = 80.8 ± 0.16 μg mL-1) compared to C. pyrenoidosa (EC50 = 631.4 ± 0.41 μg mL-1) in mono-cultures. M. aeruginosa won in the co-cultures when phenol was below or equal to 20 μg mL-1, while C. pyrenoidosa became the dominant species in the 200 μg mL-1 treatment. Photosynthetic activity was measured by a fluometer. Results showed phenol significantly impacted the photosynthetic activity of M. aeruginosa by inhibiting the acceptor side of its photosystem II (PSII), while such inhibition in C. pyrenoidosa was only observed in the highest phenol treatment (200 μg mL-1). This study provides a better understanding for predicting the succession of algal community structure in water bodies susceptible to phenolic contamination. Moreover, it reveals the mechanism on photosynthetic responses of these two species under phenolic stress. Algal cells are ubiquitous, and are sensitive to aromatic pollutants. [...]greater insights into their damaging effects on phytoplankton are crucial, given their role on primary productivity in ecosystems. [...]it has been reported that polycyclic aromatic hydrocarbons (PAHs) could also affect the algal interspecific competition [14,17]. Some organic compounds could influence the growth of Microcystis [15,19], while the detailed information about the competition between Microcystis and other algae under the stress of phenol is still unclear. [...]in this study, two common species of phytoplankton (M. aeruginosa and C. pyrenoidosa) were chosen to investigate the effects of phenol in mono- and co-cultures. The absorbance of the colored complex of phenol with 4- amino antipyrine was detected at 460 nm [26]. [...]to detect the abiotic degradation of phenol during the experiment, a blank control (BG11 medium with phenol and without algal cells) was designed to measure the concentration of phenol every two days. 2.7. The demand for phenolic compounds has been increasing rapidly, which has intensified the production and usage of phenol at a commercial scale. In some polluted water bodies, phenol has become one of the typical aromatic contaminants. Such water bodies are inescapably influenced by nutrients from human activities, and also suffer from nuisance cyanobacterial blooms. While phenolic pollution threatens water safety and ecological balance, algal cells are ubiquitous and sensitive to pollutants. Therefore, effects of phenolic pollution on interspecific competition between a bloom-forming cyanobacterium and other common alga merit quantitative investigation. In this study, the effects of phenol on ( , a bloom-forming cyanobacterium) and ( , a ubiquitous green alga) were analyzed in mono- and co-cultures. The two species were exposed to a series of phenol treatments (0, 2, 20, and 200 μg mL ). Population dynamics were measured by a flow cytometer and analyzed by the Lotka-Volterra model. The results showed that was more sensitive to phenol (EC = 80.8 ± 0.16 μg mL ) compared to (EC = 631.4 ± 0.41 μg mL ) in mono-cultures. won in the co-cultures when phenol was below or equal to 20 μg mL , while became the dominant species in the 200 μg mL treatment. Photosynthetic activity was measured by a fluometer. Results showed phenol significantly impacted the photosynthetic activity of by inhibiting the acceptor side of its photosystem II (PSII), while such inhibition in was only observed in the highest phenol treatment (200 μg mL ). This study provides a better understanding for predicting the succession of algal community structure in water bodies susceptible to phenolic contamination. Moreover, it reveals the mechanism on photosynthetic responses of these two species under phenolic stress. The demand for phenolic compounds has been increasing rapidly, which has intensified the production and usage of phenol at a commercial scale. In some polluted water bodies, phenol has become one of the typical aromatic contaminants. Such water bodies are inescapably influenced by nutrients from human activities, and also suffer from nuisance cyanobacterial blooms. While phenolic pollution threatens water safety and ecological balance, algal cells are ubiquitous and sensitive to pollutants. Therefore, effects of phenolic pollution on interspecific competition between a bloom-forming cyanobacterium and other common alga merit quantitative investigation. In this study, the effects of phenol on Microcystis aeruginosa (M. aeruginosa, a bloom-forming cyanobacterium) and Chlorella pyrenoidosa (C. pyrenoidosa, a ubiquitous green alga) were analyzed in mono- and co-cultures. The two species were exposed to a series of phenol treatments (0, 2, 20, and 200 μg mL−1). Population dynamics were measured by a flow cytometer and analyzed by the Lotka-Volterra model. The results showed that M. aeruginosa was more sensitive to phenol (EC50 = 80.8 ± 0.16 μg mL−1) compared to C. pyrenoidosa (EC50 = 631.4 ± 0.41 μg mL−1) in mono-cultures. M. aeruginosa won in the co-cultures when phenol was below or equal to 20 μg mL−1, while C. pyrenoidosa became the dominant species in the 200 μg mL−1 treatment. Photosynthetic activity was measured by a fluometer. Results showed phenol significantly impacted the photosynthetic activity of M. aeruginosa by inhibiting the acceptor side of its photosystem II (PSII), while such inhibition in C. pyrenoidosa was only observed in the highest phenol treatment (200 μg mL−1). This study provides a better understanding for predicting the succession of algal community structure in water bodies susceptible to phenolic contamination. Moreover, it reveals the mechanism on photosynthetic responses of these two species under phenolic stress. |
Author | Tan, Xiao Parajuli, Keshab Hang, Xiaoshuai Hu, Yue Duan, Zhipeng Dai, Kaiwen |
AuthorAffiliation | 2 School of Population and Global Health, Faculty of Medicine, Denistry and Health Sciences, The University of Melbourne, VIC 3010 Melbourne, Australia; kparajuli@student.unimelb.edu.au 3 Nanjing Institute of Environmental Sciences, Ministry of Ecology and Environment, Nanjing 210042, China; hxs@nies.org 1 Key Laboratory of Integrated Regulation and Resource Development on Shallow Lakes, Ministry of Education, College of Environment, Hohai University, Nanjing 210098, China; algaegroup@163.com (K.D.); duanzhipeng@hhu.edu.cn (Z.D.); 1714060112@hhu.edu.cn (Y.H.) |
AuthorAffiliation_xml | – name: 1 Key Laboratory of Integrated Regulation and Resource Development on Shallow Lakes, Ministry of Education, College of Environment, Hohai University, Nanjing 210098, China; algaegroup@163.com (K.D.); duanzhipeng@hhu.edu.cn (Z.D.); 1714060112@hhu.edu.cn (Y.H.) – name: 2 School of Population and Global Health, Faculty of Medicine, Denistry and Health Sciences, The University of Melbourne, VIC 3010 Melbourne, Australia; kparajuli@student.unimelb.edu.au – name: 3 Nanjing Institute of Environmental Sciences, Ministry of Ecology and Environment, Nanjing 210042, China; hxs@nies.org |
Author_xml | – sequence: 1 givenname: Xiao surname: Tan fullname: Tan, Xiao – sequence: 2 givenname: Kaiwen surname: Dai fullname: Dai, Kaiwen – sequence: 3 givenname: Keshab surname: Parajuli fullname: Parajuli, Keshab – sequence: 4 givenname: Xiaoshuai surname: Hang fullname: Hang, Xiaoshuai – sequence: 5 givenname: Zhipeng surname: Duan fullname: Duan, Zhipeng – sequence: 6 givenname: Yue surname: Hu fullname: Hu, Yue |
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CitedBy_id | crossref_primary_10_1007_s11356_023_26249_1 crossref_primary_10_3390_antiox10101582 crossref_primary_10_1016_j_jclepro_2023_137635 crossref_primary_10_1007_s11356_020_10979_7 crossref_primary_10_1016_j_eti_2021_101463 crossref_primary_10_3390_w13101346 crossref_primary_10_1007_s11356_022_21537_8 crossref_primary_10_1016_j_aquatox_2022_106084 crossref_primary_10_1016_j_ecoleng_2023_107098 |
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Keywords | interspecific competition green algae cyanobacteria Lotka-Volterra model phenol dominance establishment photosynthetic activity |
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Snippet | The demand for phenolic compounds has been increasing rapidly, which has intensified the production and usage of phenol at a commercial scale. In some polluted... Algal cells are ubiquitous, and are sensitive to aromatic pollutants. [...]greater insights into their damaging effects on phytoplankton are crucial, given... |
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SubjectTerms | Algae Aquatic ecosystems Chlorella - drug effects Chlorella - physiology Competition Experiments Growth models Microcystis - drug effects Microcystis - physiology Phenols Phenols - toxicity Photosynthesis - drug effects Pollutants Pollution Species Specificity Variance analysis Water Pollutants, Chemical - toxicity |
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Title | Effects of Phenolic Pollution on Interspecific Competition between Microcystis aeruginosa and Chlorella pyrenoidosa and their Photosynthetic Responses |
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