Paper · 2024 · PLoS ONE

Phytotoxicity risk assessment of diuron residues in sands on wheat, chickpea, and canola

Win Win Pyone; Richard W. Bell; Michael T. Rose; et al.

13
claims
25
verbatim quotes
4
citations
3
research areas
✓
Open access · cc-by

Abstract

While diuron residues are being detected more frequently in agricultural soils, there is limited information available regarding their potential phytotoxicity to non-target grain crops. This study aims to determine robust phytotoxicity thresholds for three common, but contrasting, crop species (canola, chickpea, and wheat) exposed to a range of diuron concentrations and to determine how loamy sand soil can change the toxicity thresholds relative to an inert sand. The log-logistic non-linear regression model proved most effective in determining toxicity thresholds by analysing crop responses to diuron. Canola was the most sensitive to diuron in sand followed by wheat and chickpea. Diuron exhibits higher phytotoxicity in sand compared to loamy sand, with ED50 values (which is the dose at which diuron causes a 50% decrease in plant growth) of 0.03 mg kg-1 and 0.07 mg kg-1 for canola shoot biomass inhibition and 0.01 mg kg-1 and 0.06 mg kg-1 for root dry weight reduction, respectively. The ED50 values for wheat shoot biomass (0.11 and 0.24 mg kg-1) in sand and loamy sand, respectively, and the ED50 values for root growth inhibition are 0.14 mg kg-1 in sand and 0.19 mg kg-1 in loamy sand. These values were lower than label concentrations and previously estimated average and maximum diuron residue loads (0.17 and 0.29 mg kg-1) in Western Australia paddocks. The larger ED50 values of diuron in the loamy sand can be attributed to higher soil organic matter and cation exchange capacity that decreased bio-available diuron levels. Average diuron residue loads in Western Australia crop fields exceed the ED50 value emphasizes the need for careful planning of crop rotations to avoid crop phytotoxicity from soil-borne diuron residues. Further study is needed to determine the effect of a wider range of soil properties such as pH, clay content, and soil organic matter on the phytotoxicity risk of diuron to rotational crops.

Abstract from the paper’s OpenAlex record; open copy licensed cc-by. Read at the source ↗

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Claims 13

Intervention effectobservedoriginal resultnegativemeasured

Claim · model-written summary

Canola was the most sensitive of the three crops to diuron in sand.

Treatment
diuron in sande1
Outcome
most sensitivee1
Direction
most sensitivee1
Comparator
wheat and chickpeae1

Organisms pictured · Representative pictures of the matched species, not figures from the paper.

Brassica napus var. napus
Brassica napus var. napus · Taxoncontri from Yonezawa-Shi, Yamagata, Japan · CC BY-SA 2.0 · Wikimedia Commons ↗

Verbatim

t0

“wheat, chickpea, and canola”

✓ located verbatim in the source · title, characters 61–88 · show in text ↑
e1

“Canola was the most sensitive to diuron in sand followed by wheat and chickpea”

✓ located verbatim in the source · abstract, characters 609–687 · show in text ↑
Observationobservedoriginal resultmeasured

Claim · model-written summary

The ED50 for canola shoot biomass inhibition in sand was 0.03 mg/kg.

Outcome
canola shoot biomass inhibitione2
Value
0.03 mg kg-1e2
Setting
sande2

Organisms pictured · Representative pictures of the matched species, not figures from the paper.

Brassica napus var. napus
Brassica napus var. napus · Taxoncontri from Yonezawa-Shi, Yamagata, Japan · CC BY-SA 2.0 · Wikimedia Commons ↗

Verbatim

t0

“wheat, chickpea, and canola”

✓ located verbatim in the source · title, characters 61–88 · show in text ↑
e2

“Diuron exhibits higher phytotoxicity in sand compared to loamy sand, with ED50 values (which is the dose at which diuron causes a 50% decrease in plant growth) of 0.03 mg kg-1 and 0.07 mg kg-1 for canola shoot biomass inhibition and 0.01 mg kg-1 and 0.06 mg kg-1 for root dry weight reduction, respectively”

✓ located verbatim in the source · abstract, characters 689–995 · show in text ↑
Observationobservedoriginal resultmeasured

Claim · model-written summary

The ED50 for canola shoot biomass inhibition in loamy sand was 0.07 mg/kg.

Outcome
canola shoot biomass inhibitione2
Value
0.07 mg kg-1e2
Setting
loamy sande2

Organisms pictured · Representative pictures of the matched species, not figures from the paper.

Brassica napus var. napus
Brassica napus var. napus · Taxoncontri from Yonezawa-Shi, Yamagata, Japan · CC BY-SA 2.0 · Wikimedia Commons ↗

Verbatim

t0

“wheat, chickpea, and canola”

✓ located verbatim in the source · title, characters 61–88 · show in text ↑
e2

“Diuron exhibits higher phytotoxicity in sand compared to loamy sand, with ED50 values (which is the dose at which diuron causes a 50% decrease in plant growth) of 0.03 mg kg-1 and 0.07 mg kg-1 for canola shoot biomass inhibition and 0.01 mg kg-1 and 0.06 mg kg-1 for root dry weight reduction, respectively”

✓ located verbatim in the source · abstract, characters 689–995 · show in text ↑
Observationobservedoriginal resultmeasured

Claim · model-written summary

The ED50 for canola root dry weight reduction in sand was 0.01 mg/kg.

Outcome
root dry weight reductione2
Value
0.01 mg kg-1e2
Setting
sande2

Organisms pictured · Representative pictures of the matched species, not figures from the paper.

Brassica napus var. napus
Brassica napus var. napus · Taxoncontri from Yonezawa-Shi, Yamagata, Japan · CC BY-SA 2.0 · Wikimedia Commons ↗

Verbatim

t0

“wheat, chickpea, and canola”

✓ located verbatim in the source · title, characters 61–88 · show in text ↑
e2

“Diuron exhibits higher phytotoxicity in sand compared to loamy sand, with ED50 values (which is the dose at which diuron causes a 50% decrease in plant growth) of 0.03 mg kg-1 and 0.07 mg kg-1 for canola shoot biomass inhibition and 0.01 mg kg-1 and 0.06 mg kg-1 for root dry weight reduction, respectively”

✓ located verbatim in the source · abstract, characters 689–995 · show in text ↑
Observationobservedoriginal resultmeasured

Claim · model-written summary

The ED50 for canola root dry weight reduction in loamy sand was 0.06 mg/kg.

Outcome
root dry weight reductione2
Value
0.06 mg kg-1e2
Setting
loamy sande2

Organisms pictured · Representative pictures of the matched species, not figures from the paper.

Brassica napus var. napus
Brassica napus var. napus · Taxoncontri from Yonezawa-Shi, Yamagata, Japan · CC BY-SA 2.0 · Wikimedia Commons ↗

Verbatim

t0

“wheat, chickpea, and canola”

✓ located verbatim in the source · title, characters 61–88 · show in text ↑
e2

“Diuron exhibits higher phytotoxicity in sand compared to loamy sand, with ED50 values (which is the dose at which diuron causes a 50% decrease in plant growth) of 0.03 mg kg-1 and 0.07 mg kg-1 for canola shoot biomass inhibition and 0.01 mg kg-1 and 0.06 mg kg-1 for root dry weight reduction, respectively”

✓ located verbatim in the source · abstract, characters 689–995 · show in text ↑
Observationobservedoriginal resultmeasured

Claim · model-written summary

The ED50 for wheat shoot biomass was 0.11 mg/kg in sand and 0.24 mg/kg in loamy sand.

Outcome
wheat shoot biomasse3
Value
0.11 and 0.24 mg kg-1e3
Setting
sand and loamy sande3

Organisms pictured · Representative pictures of the matched species, not figures from the paper.

Triticum aestivum
Triticum aestivum · TaxonRasbak · CC BY-SA 3.0 · Wikimedia Commons ↗

Verbatim

t0

“wheat, chickpea, and canola”

✓ located verbatim in the source · title, characters 61–88 · show in text ↑
e3

“The ED50 values for wheat shoot biomass (0.11 and 0.24 mg kg-1) in sand and loamy sand, respectively, and the ED50 values for root growth inhibition are 0.14 mg kg-1 in sand and 0.19 mg kg-1 in loamy sand”

✓ located verbatim in the source · abstract, characters 997–1201 · show in text ↑
Observationobservedoriginal resultmeasured

Claim · model-written summary

The ED50 for wheat root growth inhibition in sand was 0.14 mg/kg.

Outcome
root growth inhibitione3
Value
0.14 mg kg-1e3
Setting
in sande3

Organisms pictured · Representative pictures of the matched species, not figures from the paper.

Triticum aestivum
Triticum aestivum · TaxonRasbak · CC BY-SA 3.0 · Wikimedia Commons ↗

Verbatim

t0

“wheat, chickpea, and canola”

✓ located verbatim in the source · title, characters 61–88 · show in text ↑
e3

“The ED50 values for wheat shoot biomass (0.11 and 0.24 mg kg-1) in sand and loamy sand, respectively, and the ED50 values for root growth inhibition are 0.14 mg kg-1 in sand and 0.19 mg kg-1 in loamy sand”

✓ located verbatim in the source · abstract, characters 997–1201 · show in text ↑
Observationobservedoriginal resultmeasured

Claim · model-written summary

The ED50 for wheat root growth inhibition in loamy sand was 0.19 mg/kg.

Outcome
root growth inhibitione3
Value
0.19 mg kg-1e3
Setting
in loamy sande3

Organisms pictured · Representative pictures of the matched species, not figures from the paper.

Triticum aestivum
Triticum aestivum · TaxonRasbak · CC BY-SA 3.0 · Wikimedia Commons ↗

Verbatim

t0

“wheat, chickpea, and canola”

✓ located verbatim in the source · title, characters 61–88 · show in text ↑
e3

“The ED50 values for wheat shoot biomass (0.11 and 0.24 mg kg-1) in sand and loamy sand, respectively, and the ED50 values for root growth inhibition are 0.14 mg kg-1 in sand and 0.19 mg kg-1 in loamy sand”

✓ located verbatim in the source · abstract, characters 997–1201 · show in text ↑
Associationobservedoriginal resultnegativemeasured

Claim · model-written summary

Diuron phytotoxicity was higher in sand than in loamy sand.

Treatment
diurone2
Outcome
phytotoxicitye2
Direction
highere2
Comparator
loamy sande2
Setting
in sande2

Organisms pictured · Representative pictures of the matched species, not figures from the paper.

Cicer arietinum
Cicer arietinum · TaxonSanjay Acharya · CC BY-SA 3.0 · Wikimedia Commons ↗
Triticum aestivum
Triticum aestivum · TaxonRasbak · CC BY-SA 3.0 · Wikimedia Commons ↗
Brassica napus var. napus
Brassica napus var. napus · Taxoncontri from Yonezawa-Shi, Yamagata, Japan · CC BY-SA 2.0 · Wikimedia Commons ↗

Verbatim

t0

“wheat, chickpea, and canola”

✓ located verbatim in the source · title, characters 61–88 · show in text ↑
e2

“Diuron exhibits higher phytotoxicity in sand compared to loamy sand, with ED50 values (which is the dose at which diuron causes a 50% decrease in plant growth) of 0.03 mg kg-1 and 0.07 mg kg-1 for canola shoot biomass inhibition and 0.01 mg kg-1 and 0.06 mg kg-1 for root dry weight reduction, respectively”

✓ located verbatim in the source · abstract, characters 689–995 · show in text ↑
Mechanismauthor interpretationoriginal resultbasis n/a

Claim · model-written summary

The larger ED50 values in loamy sand are attributed to higher soil organic matter and cation exchange capacity, which reduced bio-available diuron.

Outcome
larger ED50 valuese5
Qualifier
higher soil organic matter and cation exchange capacitye5

Organisms pictured · Representative pictures of the matched species, not figures from the paper.

Cicer arietinum
Cicer arietinum · TaxonSanjay Acharya · CC BY-SA 3.0 · Wikimedia Commons ↗
Triticum aestivum
Triticum aestivum · TaxonRasbak · CC BY-SA 3.0 · Wikimedia Commons ↗
Brassica napus var. napus
Brassica napus var. napus · Taxoncontri from Yonezawa-Shi, Yamagata, Japan · CC BY-SA 2.0 · Wikimedia Commons ↗

Verbatim

t0

“wheat, chickpea, and canola”

✓ located verbatim in the source · title, characters 61–88 · show in text ↑
e5

“The larger ED50 values of diuron in the loamy sand can be attributed to higher soil organic matter and cation exchange capacity that decreased bio-available diuron levels”

✓ located verbatim in the source · abstract, characters 1374–1544 · show in text ↑
Associationobservedoriginal resultnegativemeasured

Claim · model-written summary

The ED50 values were lower than label concentrations and estimated average and maximum diuron residue loads in Western Australia paddocks.

Outcome
These valuese4
Direction
lowere4
Comparator
label concentrationse4
Setting
Western Australia paddockse4

Organisms pictured · Representative pictures of the matched species, not figures from the paper.

Cicer arietinum
Cicer arietinum · TaxonSanjay Acharya · CC BY-SA 3.0 · Wikimedia Commons ↗
Triticum aestivum
Triticum aestivum · TaxonRasbak · CC BY-SA 3.0 · Wikimedia Commons ↗
Brassica napus var. napus
Brassica napus var. napus · Taxoncontri from Yonezawa-Shi, Yamagata, Japan · CC BY-SA 2.0 · Wikimedia Commons ↗

Verbatim

t0

“wheat, chickpea, and canola”

✓ located verbatim in the source · title, characters 61–88 · show in text ↑
e4

“These values were lower than label concentrations and previously estimated average and maximum diuron residue loads (0.17 and 0.29 mg kg-1) in Western Australia paddocks”

✓ located verbatim in the source · abstract, characters 1203–1372 · show in text ↑
Recommendationauthor interpretationoriginal resultbasis n/a

Claim · model-written summary

Average diuron residue loads in Western Australia crop fields exceed the ED50 value, so crop rotations need careful planning to avoid phytotoxicity.

Outcome
careful planning of crop rotationse6
Qualifier
Average diuron residue loads in Western Australia crop fields exceed the ED50 valuee6

Organisms pictured · Representative pictures of the matched species, not figures from the paper.

Cicer arietinum
Cicer arietinum · TaxonSanjay Acharya · CC BY-SA 3.0 · Wikimedia Commons ↗
Triticum aestivum
Triticum aestivum · TaxonRasbak · CC BY-SA 3.0 · Wikimedia Commons ↗
Brassica napus var. napus
Brassica napus var. napus · Taxoncontri from Yonezawa-Shi, Yamagata, Japan · CC BY-SA 2.0 · Wikimedia Commons ↗

Verbatim

t0

“wheat, chickpea, and canola”

✓ located verbatim in the source · title, characters 61–88 · show in text ↑
e6

“Average diuron residue loads in Western Australia crop fields exceed the ED50 value emphasizes the need for careful planning of crop rotations to avoid crop phytotoxicity from soil-borne diuron residues”

✓ located verbatim in the source · abstract, characters 1546–1748 · show in text ↑
Method / resourceobservedoriginal resultpositivemeasured

Claim · model-written summary

The log-logistic non-linear regression model was the most effective of the models for determining diuron toxicity thresholds.

Outcome
toxicity thresholdse7
Comparator
most effectivee7

Schema note from the model: no other model is named; the ranking phrase is used as the comparator

Verbatim

e7

“The log-logistic non-linear regression model proved most effective in determining toxicity thresholds by analysing crop responses to diuron”

✓ located verbatim in the source · abstract, characters 468–607 · show in text ↑