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Diuron

Diuron is a herbicide used for the control of annual and perennial weeds.
It is a phenylurea compound that inhibits photosynthesis by blocking electron transport in photosystem II.
Diuron is used in a variety of agricultural and industrial applications, including weed management in crops, landscaping, and aquatic environments.
Researchers studying the effects and uses of diuron can utilize PubCompare.ai to optimize their research by accessing relevant protocols from the literature, preprints, and patents, enabling enhanced reproducibilty and accuracy in their diuron-focused studies.

Most cited protocols related to «Diuron»

TW samples were analyzed by USGS using 12 target organic (482 unique analytes) and 1 inorganic (19 analytes) methods (Table S1).63 (link) Analyses conducted at 3 USGS laboratories included the (1) National Water Quality Laboratory (NWQL) in Denver, Colorado (volatile organic compounds (VOC);64 (link) steroid hormones and related compounds;65 organic wastewater indicator (OWI) compounds;66 (link) human-use pharmaceuticals, pharmaceutical metabolites, and polar organic compounds;67 (link) and trace elements68 ,69 ); (2) Organic Geochemistry Research Laboratory (OGRL) in Lawrence, Kansas (acetamide herbicides and degradation products;70 glyphosate, glufosinate, and aminomethylphosphonic acid;71 steroid hormones and phytoestrogens;72 (link) triazine and phenylurea herbicides;73 and antibiotics74 ); and (3) Organic Chemistry Research Laboratory (OCRL) in Sacramento, California (pesticide and pesticide degradates;75 (link) diuron, diuron degradates, and neonicotinoid insecticides; 76 and DBP77 (link)). Per/polyfluoroalkyl substances (PFAS) were analyzed78 (link)−80 at the EPA, Colorado School of Mines (CSM), and NWQL. Pharmaceutical samples were syringe filtered (0.7 μm nominal pore size, glass fiber) in the field. Pharmaceutical and VOC bottles were pretreated with ascorbic acid to neutralize chlorine/chloramine. In vitro estrogen (ER), androgen (AR), and glucocorticoid (GR) activities were assessed by EPA34 (link),55 (link) and USGS.34 (link),55 (link),81 (link) Results are in Tables S2S5 and at Romanok et al.82 (link)
Publication 2018
acetamide aminomethylphosphonic acid (AMPA) Androgens Ascorbic Acid chloramine Chlorine Diuron Estrogens Glucocorticoids glufosinate glyphosate Herbicides Homo sapiens Hormones Insecticides Neonicotinoids Organic Chemicals Pesticides Pharmaceutical Preparations Phytoestrogens Steroids Syringes Triazines Volatile Organic Compounds
Nearshore coastal seawater was collected at the Australian Institute of Marine Science (19°16’ S, 147° 03’ E), Cape Cleveland, QLD under the permit G12/35236.1 issued by the Great Barrier Reef Marine Park Authority. The seawater was filtered to 0.45 μm to remove all particulates and added to individual 500 ml Erlenmeyer flasks (300 ml final volume). The sample treatments were spiked to a final concentration of ~10 μg l-1 for each herbicide (Table 2) and the flasks stoppered with autoclaved cotton bungs to allow for aerobic conditions. Herbicide standards (98.5–99.9%) were purchased from Sigma-Aldrich, added to 2 ml of the carrier solvent ethanol (to assist in solubility), and made to 5 mg l-1 concentration with Milli-Q water. The same volume of ethanol (final less than 0.03% v/v) was added to all flasks, including controls for consistency between treatments. Triplicate flasks were shaken at 25°C and 100 rpm in the dark using an Innova 44, incubator shaker. One series of flasks contained a mixture of the six PSII herbicides (ametryn, atrazine, diuron, hexazinone, simazine, tebuthiuron) and the second series of flasks the same herbicide mixture with the addition of 45 mg l-1 mercuric chloride (MC) to eliminate microbial activity (Table 2) [28 ]. Sample treatment flasks were weighed before sampling to monitor evaporation losses for concentration adjustments. Flasks were topped up with fresh sterile water (Milli-Q) and any losses were compensated for during calculations. Experiment 1 (pilot) examined the degradation of six PSII herbicides over 60 d (Table 2). The 60 day experiment length was set as the maximum by following the OECD method. The purpose of this experiment was to test whether bacteria contributed to biodegradation of these herbicides. Microbial activity is eliminated in the presence of MC and to inform the second experiment which was to be conducted over a longer period.
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Publication 2015
ametryne Atrazine Bacteria Bacteria, Aerobic Diuron Environmental Biodegradation Ethanol Gossypium Herbicides hexazinone Marines Mercuric Chloride Simazine Solvents Specimen Handling Sterility, Reproductive tebuthiuron
Above mentioned cell lines were transiently co-transfected with the pGL4.37[luc2P/ARE/Hygro] plasmid and the Renilla plasmid using FHD (Promega, Madison, USA) for Pac2 and ZF4, and XHP (Roche, Mannheim, Germany) for ZFL. Subsequently, after exposure to known Nrf2 inducers or pesticides, Nrf2 induction was analyzed using a Dual-Luciferase® Reporter (DLR™) assay (Promega, Madison, USA). Cells were seeded into white, clear-bottom 96-well plates (Corning, New York, USA) at a density of 104 cellls/well for Pac2, 1.25*104 cells/well for ZF4, and 2.5*104 cells/well for ZFL in 100 µl/well. After 24 h of incubation, cells reached a confluency of about 80%. Transient transfection using FHD or XHP, respectively was conducted in a 2 µg reagent to 1.2 µg DNA (0.9 µg reporter plasmid, 0.3 µg control plasmid) ratio, according to the manufacturer’s instructions. After 24 h of post-transfection incubation, cells were exposed to postulated Nrf2 inducers or pesticides. Prepared stock solutions (see section “Chemicals”) were further diluted using the cell type specific nutrition medium (see section “Cell culture”) supplemented with 5‰ EtOH as a solvent. Seeded cells on 96-well plates were either exposed in technical quadruplicates to increasing concentrations (0.1 µM, 1 µM, 10 µM, 100 µM) of postulated Nrf2 inducers tBHQ, SFN, and H2O2 or to increasing concentrations (6.25 µM, 12.5 µM, 25 µM, 50 µM, 100 µM) of the pesticides atrazine, deltamethrin, diazinon, diuron, metazachlor, and terbutylazine. Double quadruplicates of 5‰ EtOH solvent-nutrition medium were used as controls. In parallel with the oxidative stress exposure, increasing DMSO concentrations (1%, 4%, 7%, and 10% v/v) were tested as a cytotoxic control. After 24 h incubation, cells were lysed and quantitative Nrf2-dependent luminescence was measured via Dual-Luciferase® Reporter assay according to the manufacturer’s protocol using an auto-injecting Infinite M1000 microplate reader (Tecan, Männedorf, Switzerland). The luciferase activity was expressed as fold change compared to the controls.
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Publication 2018
2-tert-butylhydroquinone Atrazine Biological Assay Cell Culture Techniques Cell Lines Cells decamethrin Diazinon Diuron Ethanol Luciferases Luminescence metazachlor NFE2L2 protein, human Oxidative Stress Paragangliomas 4 Peroxide, Hydrogen Pesticides Plasmids Promega Sea Pansy Solvents Sulfoxide, Dimethyl terbutylazine Transfection Transients
All animals were from clonal population CC7 (Sunagawa et al. 2009 (link)), which in spawning experiments typically behaves as a male (S. F. Perez and J. R. Pringle, unpublished data). For experiments performed at Stanford, the stock cultures were grown in a circulating artificial sea water (ASW) system at ∼25° with 20 to 40 µmol photons m−2 s−1 of photosynthetically active radiation on an ∼12-hr light/12-hr dark (12L:12D) cycle and fed freshly hatched brine shrimp nauplii approximately twice per week. To generate aposymbiotic anemones, animals were placed in a separate polycarbonate tub and subjected to several repetitions of the following process: cold-shocking by addition of 4° ASW and incubation at 4° for 4 hr, followed by 1–2 days of treatment at ∼25° in ASW containing the photosynthesis inhibitor Diuron (Sigma-Aldrich D2425) at 50 µM (lighting approximately as noted above). After recovery for several weeks in ASW at ∼25° in the light (as noted above) with feeding (as noted above, with water changes on the days following feeding), putatively aposymbiotic anemones were inspected by fluorescence microscopy to confirm the complete absence of dinoflagellates (whose bright chlorophyll autofluorescence is conspicuous when they are present).
For experiments performed at Cornell, anemones were grown in incubators at 25° in ASW in 1-liter glass bowls and fed (as noted above) approximately three times per week. Symbiotic anemones were kept on a 12L:12D cycle at 18 to 22 µmol photons m−2 s−1 of photosynthetically active radiation. Aposymbiotic animals were generated by exposing anemones under the same lighting and feeding regimen to 50 µM Diuron in ASW, with daily water changes, for ∼30 d or until the anemones were devoid of algae, as confirmed by fluorescence microscopy. After bleaching, aposymbiotic anemones were maintained in the dark for ∼2 yr (with feeding as noted above) before experimentation.
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Publication 2013
Anemone Animals Artemia Chlorophyll Clone Cells Cold Temperature Dinoflagellates Diuron Light Males Microscopy, Fluorescence Photosynthesis polycarbonate Radiation Symbiosis Treatment Protocols
Lugol’s iodine preserved cells were enumerated using a Beckman Coulter Multisizer™ 3 Coulter Counter® with a 50 µm aperture which allowed cell densities to be quantified with a relative standard deviation of 3%. Cell densities of selected samples were verified microscopically with a hemacytometer. Growth rates were calculated for each day of the experiment based upon changes in cell abundance according to the equation µ = Ln(N2/N1)/(t2–t1) where N1 and N2 equal the biomass at time 1 (t1) and time 2 (t2) respectively [54] . Nitrate was analyzed by reducing the nitrate to nitrite using spongy cadmium as per Jones [55] . Ammonium and phosphate were analyzed using techniques modified from Parsons et al[56] . Total dissolved N and P were analyzed using persulfate digestion techniques from Valderrama [57] . Urea was analyzed according to Price and Harrison [58] . These nutrient analyses provided 100±10% recovery of standard reference material (SPEX CertiPrep™) for nitrate, ammonium, phosphate, total dissolved N, and total dissolved P. Whole water samples were analyzed for the hepatoxin microcystin by first freezing samples at −80°C for 24 h and then lysing the cells using an Abraxis QuikLyse™ Cell Lysis kit for Microcystins/Nodularins ELISA Microtiter Plate according to the manufacturer’s instructions. Lysed samples were then analyzed with a colorimetric immunoassay using an Abraxis Microcystins/Nodularins (ADDA) ELISA Kit according to the manufacturer’s instructions [59] (link). This method provided an analytical precision of ±2% and a 96±2% recovery of spiked samples. Bulk alkaline phosphatase activity was measured for each replicate experimental sample on a Turner Designs TD-700 fluorometer (EM filter of 410–600 nm and EX filter of 300–400 nm) using 4-Methylumbelliferone phosphate (250-µM concentration) as the substrate [60] . Alkaline phosphatase activity measured by this assay has been shown to be significantly correlated with the expression of the gene encoding for alkaline phosphatase (phoX) in Microcystis aeruginosa LE-3 (p<0.005) [34] (link) and provided an analytical precision of ±4%. Maximum quantum efficiency of photosystem II (PSII) was estimated from in vivo (Fi) and DCMU (3,4-dichlorophenyl-1,1-dimethylurea)-enhanced in vivo fluorescence (Fm) of each replicate experimental sample on a Turner Designs TD-700 fluorometer (EM filter of >665 nm and EX filter of 340–500 nm). All readings were blank corrected using BG-11 media. DCMU blocks electron transfer between PSII and PSI and yields maximal fluorescence and previous studies have demonstrated that Fv/Fm can be a sensitive diagnostic of nutrient limitation, reaching a maximal value of ∼ 0.65 under nutrient replete conditions, and decreasing to less than half of that under nutrient limitation [61] (link).
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Publication 2013
Alkaline Phosphatase Ammonium Biological Assay Cadmium Cells Colorimetry Diagnosis Dietary Fiber Digestion Diuron Electron Transport Enzyme-Linked Immunosorbent Assay Fluorescence Gene Expression Hymecromone Immunoassay Lugol's solution microcystin Microcystins Microcystis aeruginosa Nitrates Nitrites nodularin Nutrients Phosphates Photosystem II Porifera Urea

Most recents protocols related to «Diuron»

Not available on PMC !

Example 11

Media was selected for use and kill curves developed as specified above. For selection, different techniques were utilized. Either a step wise selection was applied, or an immediate lethal level of herbicide was applied. In either case, all of the calli were transferred for each new round of selection. Selection was 4-5 cycles of culture with 3-5 weeks for each cycle. Cali were placed onto nylon membranes to facilitate transfer (200 micron pore sheets, Biodesign, Saco, Maine). Membranes were cut to fit 100×20 mm Petri dishes and were autoclaved prior to use 25-35 calli (average weight/calli being 22 mg) were utilized in every plate. In addition, one set of calli were subjected to selection in liquid culture media with weekly subcultures followed by further selection on semi-solid media. Mutant lines were selected using saflufenacil, 1,5-dimethyl-6-thioxo-3-(2,2,7-trifluoro-3-oxo-4-(prop-2-ynyl)-3,4-dihydro-2H-benzo[b][1,4]oxazin-6-yl)-1,3,5-triazinane-2,4-dione (CAS 1258836-72-4), flumioxazin, butafenacil, acifluorfen, lactofen, bifenox, sulfentrazone, and photosynthesis inhibitor diuron as negative control. Efficiencies of obtaining mutants was high either based on a percentage of calli that gave rise to a regenerable, mutant line or the number of lines as determined by the gram of tissue utilized.

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Patent 2024
acifluorfen bifenox butafenacil Callosities Culture Media Diuron flumioxazin Herbicides Hyperostosis, Diffuse Idiopathic Skeletal lactofen N'-(2-chloro-4-fluoro-5-(3-methyl-2,6-dioxo-4(trifluoromethyl)-3,6-dihydro-1(2H)-pyrimidinyl)benzoyl)-N-isopropyl-N-methylsulfamide N-(2,4-dichloro-5-(4-(difluoromethyl)-4,5-dihydro-3-methyl-5-oxo-1H-1,2,4-triazol-1-yl)phenyl)methanesulfonamide N-methylacetamide-oxotremorine M Nylons Photosynthesis Tissue, Membrane Tissues
Not available on PMC !

Example 11

Media is selected for use and kill curves developed as specified above. For selection, different techniques are utilized. Either a step wise selection is applied, or an immediate lethal level of herbicide is applied. In either case, all of the calli are transferred for each new round of selection. Selection is 4-5 cycles of culture with 3-5 weeks for each cycle. Cali are placed onto nylon membranes to facilitate transfer (200 micron pore sheets, Biodesign, Saco, Maine). Membranes are cut to fit 100×20 mm Petri dishes and are autoclaved prior to use 25-35 calli (average weight/calli being 22 mg) are utilized in every plate. In addition, one set of calli are subjected to selection in liquid culture media with weekly subcultures followed by further selection on semi-solid media. Mutant lines are selected using saflufenacil, 1,5-dimethyl-6-thioxo-3-(2,2,7-trifluoro-3-oxo-4-(prop-2-ynyl)-3,4-dihydro-2H-benzo[b][1,4]oxazin-6-yl)-1,3,5-triazinane-2,4-dione (CAS 1258836-72-4/trifludimoxazin), flumioxazin, butafenacil, acifluorfen, lactofen, bifenox, sulfentrazone, and photosynthesis inhibitor diuron as negative control. Efficiencies of obtaining mutants is high either based on a percentage of calli that gave rise to a regenerable, mutant line or the number of lines as determined by the gram of tissue utilized.

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Patent 2024
acifluorfen bifenox butafenacil Callosities Culture Media Diuron flumioxazin Herbicides Hyperostosis, Diffuse Idiopathic Skeletal lactofen N'-(2-chloro-4-fluoro-5-(3-methyl-2,6-dioxo-4(trifluoromethyl)-3,6-dihydro-1(2H)-pyrimidinyl)benzoyl)-N-isopropyl-N-methylsulfamide N-(2,4-dichloro-5-(4-(difluoromethyl)-4,5-dihydro-3-methyl-5-oxo-1H-1,2,4-triazol-1-yl)phenyl)methanesulfonamide N-methylacetamide-oxotremorine M Nylons Photosynthesis Tissue, Membrane Tissues
Chlorophyll fluorescence kinetics were measured at room temperature on dark-adapted cells. A home-built fluorimeter with a green detecting light was used for measurements on 1-ml aliquots of liquid cultures (56 (link)) before and after the addition of PSII-specific inhibitor 3-(3,4-dichlorophenyl)-1,1-dimethylurea (DCMU; 10 μM). A fluorescence imaging system (BeamBio, SpeedZen camera) with a blue detecting light was used for measurements of plates as described (57 (link)). The maximum quantum yield of PSII photochemistry (Fv/Fm) was calculated as (Fm-F0)/Fm, where F0 is the fluorescence level of dark-adapted cells in the absence of DCMU and Fm is the maximum level of fluorescence in the presence of DCMU or after a saturating light pulse.
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Publication 2023
Chlorophyll Diuron Fluorescence Kinetics Light Methyl Green Pulse Rate
For evaluation of CEF activity, P700+ re-reduction and the redox kinetics of P700 were determined according to previously described methods65 (link),66 (link) with some modifications. Briefly, Synechococcus cells were cultured in BG11 medium at an initial OD730 of 0.05 in column photobioreactors and cultivated in MC1000 under 30 °C and 50 μmol photons/m2/s bubbled with air. Cells in the mid-log phase were harvested and adjusted to approximately 6 × 109 cells in 3 mL and were dark-acclimated for 20 min at room temperature (23 °C). P700 redox was monitored after the termination of AL illumination (2800 μE/m2/s for 35 s) under a background of FR light (Intensity level 20) using Dual-PAM 100 (Heinz Walz) (Dual PAM v1.19 software). The P700 levels were normalized by equating the absorbance minimum after the termination of AL illumination to 0 and equating the absorbance maximum of 3 s before the termination of AL illumination to one. The re-reduction of P700+ in darkness was measured by monitoring absorbance changes at 830 nm and using 875 nm as a reference. After dark-acclimated for 20 min, 20 μM DCMU was added to the cultures before the measurement. The P700 was oxidized by FR light (Intensity level 20) for 40 s, and the subsequent re-reduction of P700+ in the dark was monitored. The curves were normalized by equating the absorbance maximum of 1 s before termination of FR light to one. The initial rate of P700+ re-reduction was acquired from normalized curves by calculating the slope of the initial values after FR was turned off and the R2 was more than 0.99.
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Publication 2023
Cells Culture Media Darkness Diuron Kinetics Light Lighting Oxidation-Reduction Photobioreactors Synechococcus
Approximately 1.7 × 109 cells in 3 mL were dark-acclimated for 20 min at room temperature (23 °C). And the fluorescence parameters Fv/Fm (maximum quantum yield) of PSII were measured using a Dual-PAM 100 (Heinz Walz) (Dual PAM v1.19 software). A measure light intensity of 19 μE/m2/s was used and the saturating light pulse was 6000 μE/m2/s (200 ms). The maximum chlorophyll fluorescence after adding 20 μM DCMU with AL (54 μE/m2/s) was recorded as the maximum Fm.
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Publication 2023
Cells Chlorophyll Diuron Fluorescence Light Pulse Rate

Top products related to «Diuron»

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Diuron is a laboratory chemical used as a reference standard or analytical reagent. It is a crystalline solid with a molecular formula of C₉H₁₀Cl₂N₂O. Diuron has a high purity and is suitable for various analytical and research applications.
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The Dual-PAM-100 is a laboratory instrument designed for simultaneous measurement of chlorophyll a fluorescence and P700 absorbance changes. It provides reliable data on the photosynthetic performance of plants and algae.
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DMSO is a versatile organic solvent commonly used in laboratory settings. It has a high boiling point, low viscosity, and the ability to dissolve a wide range of polar and non-polar compounds. DMSO's core function is as a solvent, allowing for the effective dissolution and handling of various chemical substances during research and experimentation.
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Atrazine is a laboratory chemical used as a standard and reference material in analytical procedures. It is a herbicide compound that can be utilized for various research and development applications. Atrazine serves as a tool for calibration, method validation, and quality control in laboratory settings.
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The Clark-type oxygen electrode is a device used to measure the concentration of dissolved oxygen in a solution. It functions by using an electrochemical reaction to detect and quantify the amount of oxygen present in the sample.
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The Dual-PAM is a laboratory instrument designed to measure and analyze the photosynthetic activity of plant samples. It provides simultaneous measurement of chlorophyll fluorescence and P700 absorbance, which are two important parameters in the study of photosynthesis.
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More about "Diuron"

Diuron is a widely used herbicide, a member of the phenylurea family, that is effective in controlling a variety of annual and perennial weeds.
It works by inhibiting photosynthesis in plants, specifically by blocking electron transport in Photosystem II.
This makes it a valuable tool for weed management in various agricultural, landscaping, and aquatic settings.
Researchers studying the effects and applications of diuron can leverage the capabilities of PubCompare.ai to optimize their research process.
The platform allows them to access relevant protocols from the literature, preprints, and patents, enabling enhanced reproducibility and accuracy in their diuron-focused studies.
In addition to diuron, researchers may also be interested in related compounds and technologies, such as Dual-PAM-100, a fluorescence-based system used to measure photosynthetic activity, and DMSO, a common solvent used in diuron research.
Atrazine, another herbicide, shares some similarities with diuron in terms of its mode of action and applications.
To further support their research, scientists may utilize tools like the Clark-type oxygen electrode, which measures oxygen production or consumption, and the FP-8500, a fluorescence spectrometer that can be used to study the effects of diuron on photosynthetic processes.
The Dual-PAM system and DBMIB, a photosynthesis inhibitor, are also relevant to diuron research.
Alachlor, a related herbicide, and PU-830, a fluorescence-based system, may also be of interest to researchers working with diuron.
By incorporating these related terms and concepts, researchers can expand their understanding of diuron and its broader applications in the field of plant science and environmental management.