4.7 Article

Impacts on the seagrass, Zostera nigricaulis, from the herbicide Fusilade Forte (R) used in the management of Spartina anglica infestations

期刊

AQUATIC TOXICOLOGY
卷 195, 期 -, 页码 15-23

出版社

ELSEVIER SCIENCE BV
DOI: 10.1016/j.aquatox.2017.11.021

关键词

Zostera nigricaulis; Fluazifop-P-butyl; Acetyl-CoA carboxylase inhibitor; PAM fluorometery; Spartina management

资金

  1. West Gippsland Catchment Management Authority
  2. RMIT University

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The herbicide Fusilade Forte (R) (FF) is widely applied in agricultural weed management and in the management of the invasive saltmarsh grass, Spartina anglica (ricegrass or cordgrass). FF (active ingredient fluazifop-P acid, FPA) is selective for poaceous grasses. Its primary mode of action is inhibition of the acetyl coenzyme-A carboxylase (ACCase) specific to this taxonomic group, and its secondary mode is by promotion of oxidative stress. FF is applied to S. anglica infestations in the intertidal zone, in proximity to seagrass meadows. Despite the potential for vital seagrass ecosystems to be exposed to FF, there is limited knowledge of any potential impacts. We investigated impacts of FPA on the endemic Australian seagrass, Zostera nigricaulis, measuring ACCase activity and parameters that reflect oxidative stress: photosynthetic performance, lipid peroxidation and photosynthetic pigment content. Seagrass was exposed to FF (0.01-10 mg L-1 FPA and a control) for 7 d, followed by a 7-d recovery in uncontaminated seawater. An enzyme assay demonstrated that FPA 10 mg L-1 did not inhibit the activity of ACCase isolated from Z. nigricaulis, demonstrating that this seagrass is resistant to FF's primary mode of action. However, physiological impacts occurred following 7 days exposure to 0.1 mg L-1 FPA, including up to a 72% reduction in photosynthetic pigment concentration. After 7-d recovery, photosynthetic pigment content improved in treatment plants; however, treated plants exhibited higher levels of lipid peroxidation. This study demonstrates that while Z. nigricaulis is resistant to FF's primary mode of action, significant physiological impacts occur following 7 days exposure to 0.1 mg L-1 FPA. This study provides valuable information on the effects of FF on a non-target species that can better inform approaches to Spartina management in coastal sea grass ecosystems.

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