Effect of fluazifop-P-butyl herbicide on growth, pigment, and ultrastructure of Auxenochlorella pyrenoidosa and Raphidocelis subcapitata

The terrible intensification in global food demand predictably results in an increase in agricultural practices, with a focus on the usage of herbicides. Hence, a deeper understanding of the impact of this herbicide on aquatic ecosystems is required. The characterization of nano-emulsion of fluazifop-P-butyl (FL) and the toxic effects in both traditional and nanoforms on the growth, pigmentation and ultrastructure of the freshwater microalgae: Auxenochlorella pyrenoidosa and Raphidocelis subcapitata were studied. The prepared nano-emulsion has a particle size of 52-94 nm by transmission electron microscopy (TEM). Zeta potential recorded (38.5 mV) and polydispersity index recorded (0.394). Traditional fluazifop-P-butyl (TFL) in the case of A. pyrenoidosa exhibited median effective concentration (EC50) (10.909 ± 3.635 mg/L) (P= 0.235), while nano fluazifop-P-butyl (NFL) recorded EC50 (14.281 ± 6.251 mg/L) (P= 0.205). In the case of R. subcapitata, TFL recorded EC50 (1.174 ± 0.501 mg/L) (P= 0.105), while NFL exhibited EC50 (4.757 ± 1.755 mg/L) (P= 0.150). Exposure of R. subcapitata cells to 0.117 mg/L of TFL significantly decreased chlorophyll a level by (-)15.51% (P= 0.002) relative to control. Also, chlorophyll b content in A. pyrenoidosa cells significantly decreased upon treatment with 1.43 mg/L of NFL by (-)67.16% (P= 0.001). Carotenoid content in A. pyrenoidosa cells significantly increased after exposure to 1.09 mg/L of TFL by 108.88% (P= 0.001) compared to the control. Likewise, exposure of R. subcapitata cells to 0.117 mg/L of TFL elevated carotenoid levels by 200.57% (P < 0.001). Destroyed chloroplasts and compacted cell walls were observed through TEM when A. pyrenoidosa was exposed to 1.09 mg/L of TFL and 1.43 mg/L of NFL. Likewise, R. subcapitata cells were exposed to 0.117 mg/L of TFL and 0.476 mg/L of NFL. This study demonstrates that both conventional and nano-forms of FL endanger the integrity of the ecosystem and have adverse impacts on non-target organisms. Thus, it's crucial to follow biosafety protocols concerning non-target species before deciding to use this herbicide.

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Journal
Environmental Analysis Health and Toxicology
Published
2025-12-05
DOI
https://doi.org/10.5620/eaht.2025029
Primary Topic
Algal biology and biofuel production
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article
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article

Effect of fluazifop-P-butyl herbicide on growth, pigment, and ultrastructure of Auxenochlorella pyrenoidosa and Raphidocelis subcapitata

Khaled Y. Abdel‐Halim, Manal Mohamed Mostafa El-Abasy, Mohamed S. Abdel-Kareem, Soad M. Mohy El-Din et al.
Environmental Analysis Health and Toxicology
Algal biology and biofuel production
article

Effect of fluazifop-P-butyl herbicide on growth, pigment, and ultrastructure of Auxenochlorella pyrenoidosa and Raphidocelis subcapitata

Khaled Y. Abdel‐Halim, Manal Mohamed Mostafa El-Abasy, Mohamed S. Abdel-Kareem, Soad M. Mohy El-Din, Elsayed M. Ibrahim
article en

Abstract

The terrible intensification in global food demand predictably results in an increase in agricultural practices, with a focus on the usage of herbicides. Hence, a deeper understanding of the impact of this herbicide on aquatic ecosystems is required. The characterization of nano-emulsion of fluazifop-P-butyl (FL) and the toxic effects in both traditional and nanoforms on the growth, pigmentation and ultrastructure of the freshwater microalgae: Auxenochlorella pyrenoidosa and Raphidocelis subcapitata were studied. The prepared nano-emulsion has a particle size of 52-94 nm by transmission electron microscopy (TEM). Zeta potential recorded (38.5 mV) and polydispersity index recorded (0.394). Traditional fluazifop-P-butyl (TFL) in the case of A. pyrenoidosa exhibited median effective concentration (EC50) (10.909 ± 3.635 mg/L) (P= 0.235), while nano fluazifop-P-butyl (NFL) recorded EC50 (14.281 ± 6.251 mg/L) (P= 0.205). In the case of R. subcapitata, TFL recorded EC50 (1.174 ± 0.501 mg/L) (P= 0.105), while NFL exhibited EC50 (4.757 ± 1.755 mg/L) (P= 0.150). Exposure of R. subcapitata cells to 0.117 mg/L of TFL significantly decreased chlorophyll a level by (-)15.51% (P= 0.002) relative to control. Also, chlorophyll b content in A. pyrenoidosa cells significantly decreased upon treatment with 1.43 mg/L of NFL by (-)67.16% (P= 0.001). Carotenoid content in A. pyrenoidosa cells significantly increased after exposure to 1.09 mg/L of TFL by 108.88% (P= 0.001) compared to the control. Likewise, exposure of R. subcapitata cells to 0.117 mg/L of TFL elevated carotenoid levels by 200.57% (P < 0.001). Destroyed chloroplasts and compacted cell walls were observed through TEM when A. pyrenoidosa was exposed to 1.09 mg/L of TFL and 1.43 mg/L of NFL. Likewise, R. subcapitata cells were exposed to 0.117 mg/L of TFL and 0.476 mg/L of NFL. This study demonstrates that both conventional and nano-forms of FL endanger the integrity of the ecosystem and have adverse impacts on non-target organisms. Thus, it's crucial to follow biosafety protocols concerning non-target species before deciding to use this herbicide.

Environmental Analysis Health and ToxicologyVol. 40(4)
Central Laboratory For Agricultural Expert Systems (EG), Central Laboratory for Agricultural Climate (EG), Alexandria University (EG)
Openalex Percentile: Top 72%
Algal biology and biofuel production
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