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. 2013 Sep 30;8(9):e75798.
doi: 10.1371/journal.pone.0075798. eCollection 2013.

Phytotoxicity of four photosystem II herbicides to tropical seagrasses

Affiliations

Phytotoxicity of four photosystem II herbicides to tropical seagrasses

Florita Flores et al. PLoS One. .

Abstract

Coastal waters of the Great Barrier Reef (GBR) are contaminated with agricultural pesticides, including the photosystem II (PSII) herbicides which are the most frequently detected at the highest concentrations. Designed to control weeds, these herbicides are equally potent towards non-target marine species, and the close proximity of seagrass meadows to flood plumes has raised concerns that seagrasses may be the species most threatened by herbicides from runoff. While previous work has identified effects of PSII herbicides on the photophysiology, growth and mortality in seagrass, there is little comparative quantitative toxicity data for seagrass. Here we applied standard ecotoxicology protocols to quantify the concentrations of four priority PSII herbicides that inhibit photochemistry by 10, 20 and 50% (IC10, IC20 and IC50) over 72 h in two common seagrass species from the GBR lagoon. The photosystems of seagrasses Zosteramuelleri and Haloduleuninervis were shown to be generally more sensitive to the PSII herbicides Diuron, Atrazine, Hexazinone and Tebuthiuron than corals and tropical microalgae. The herbicides caused rapid inhibition of effective quantum yield (∆F/F m '), indicating reduced photosynthesis and maximum effective yields (Fv/Fm ) corresponding to chronic damage to PSII. The PSII herbicide concentrations which affected photosynthesis have been exceeded in the GBR lagoon and all of the herbicides inhibited photosynthesis at concentrations lower than current marine park guidelines. There is a strong likelihood that the impacts of light limitation from flood plumes and reduced photosynthesis from PSII herbicides exported in the same waters would combine to affect seagrass productivity. Given that PSII herbicides have been demonstrated to affect seagrass at environmental concentrations, we suggest that revision of environmental guidelines and further efforts to reduce PSII herbicide concentrations in floodwaters may both help protect seagrass meadows of the GBR from further decline.

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Conflict of interest statement

Competing Interests: The authors have declared that no competing interests exist.

Figures

Figure 1
Figure 1. Time taken to steady state inhibition.
Inhibition of effective quantum yield (ΔF/Fm) relative to maximum inhibition over time by (A) Diuron (10 µg l-1), Atrazine (50 µg l-1), Hexazinone (10 µg l-1) and Tebuthiuron (400 µg l-1) to Z . muelleri and (B) Diuron (10 µg l-1) to four seagrass species. Bars = ± SE, n = 4.
Figure 2
Figure 2. Concentration-response curves for two seagrasses species and four herbicides.
Percent inhibition relative to control for effective quantum yield (ΔF/Fm) and maximum potential yields (Fv/Fm) in Zostera muelleri and Halodule uninervis exposed to PSII herbicides over 72 h.

References

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