Search Results

You are looking at 11 - 20 of 720 items for :

  • phytotoxicity x
  • Refine by Access: All x
Clear All
Full access

Susan L.F. Meyer, Dilip K. Lakshman, Inga A. Zasada, Bryan T. Vinyard, and David J. Chitwood

nematicide, it was also important to determine whether it was harmful to seedlings of vegetable crops. Clove oil, and its primary constituent eugenol, have been reported to have phytotoxic effects ( Bainard et al., 2006 ; Boyd and Brennan, 2006 ; Boyd et al

Open access

Renata Goossen and Kimberly A. Williams

Home remedies for pest and disease problems experienced by plant consumers abound on blogs, forums, and social media groups. However, neither the threshold for phytotoxicity nor efficacy of most of these treatments has been subjected to evaluation

Open access

Shital Poudyal and Bert M. Cregg

of insecticides in retention ponds has the potential to induce phytotoxicity. Fungicides . Nursery managers often apply various fungicides to protect crops from a wide range of fungal diseases. Although fungicides may be effective at controlling

Free access

Kuo-Tan Li, Jacqueline K. Burns, and James P. Syvertsen

fundamental physiological responses. Temperatures below 15 °C for the first 24 h after application prevent fruit loosening ( Yuan and Burns, 2004 ). When applied by soil drenching, CMNP can cause typical herbicide-like phytotoxic symptoms on leaves of various

Full access

Amber N. Bates, Gerald M. Henry, and Cynthia B. McKenney

phytotoxicity concerns associated with many postemergence herbicides make preemergence herbicide applications even more important. Few research trials have focused on the phytotoxic effect of preemergence herbicides on evening primrose species. Richardson and

Open access

Mitchell Eicher-Sodo, Robert Gordon, and Youbin Zheng

) leaves ( Copes, 2009 ). Consistent dosing of water with H 2 O 2 leads to the exposure of crops to H 2 O 2 during irrigation events and brings the potential for a phytotoxic response if excessive concentrations are circulated. Exposure of crops to H 2 O

Full access

Safwan Shiyab

, as were their replicates. The total incubation experiment lasted for 31 d. Growth parameters measurements Percent RWC, percent phytotoxicity, SVI, and TI. For RWC analysis, plants were separated into roots and shoots. Wet plant biomass [fresh weight

Open access

Amir M. González-Delgado and Manoj K. Shukla

.). Soil samples collected on 5 Feb., 21 Mar., and 5 May 2016 (45, 90, and 135 d after application) were analyzed for indaziflam as well as indaziflam breakdown products. The trees were visually evaluated for phytotoxicity effects during their dormant and

Free access

Joyce G. Latimer and Ronald D. Oetting

Four-week-old salvia (Salvia splendens F. Sellow `Red Pillar') seedlings were treated with 0 or 50 ppm paclobutrazol, followed 5 h later by 0, 1, 2, or 4 times (0×, 1×, 2×, or 4×, respectively) the recommended label rate of bendiocarb (0.6 g a.i./liter), a carbamate insecticide. Seven days after treatment (DAT), phytotoxicity ratings increased with bendiocarb rate on all plants, but 50 ppm paclobutrazol reduced damage at 1× and 4× bendiocarb. Paclobutrazol also improved plant recovery from phytotoxicity damage at 21 DAT. Bendiocarb decreased the height of plants not treated with paclobutrazol at 7, 14, and 21 DAT. Plants treated with 40 ppm paclobutrazol had lower maximum phytotoxicity damage at 14 DAT, and even better recovery at 21 DAT than plants treated with 20 or 60 ppm paclobutrazol. Plants treated with paclobutrazol 4 days before applying bendiocarb had lower maximum phytotoxicity ratings relative to controls than plants treated 8 days before, the same day as, or 4 days after bendiocarb application. Chemical names used: β- [(4-chlorophenyl)methyl]- α -(1,1-dimethylethyl)-1 H- 1,2,4-triazole-1-ethanol (paclobutrazol); 2,2-dimethyl,1,3-benzodioxol-4-yl-methylcarbamate (bendiocarb).

Free access

F. C. Waltz and Ted Whitwell

Herbicides can runoff during storms or irrigation and contaminate ponds that are used for irrigation. Overseeded turf areas are particulary vulunerable to low concentrations of herbicides in irrigation water. A greenhouse study was conducted to determine the phytotoxic concentration of simazine in irrigation water perenial ryegrass (Lolium perenne), creeping bentgrass (Agrostis palustris), and fine fescue (Festuca rubra). Irrigation of 6.5 mm of herbicide contaminated and uncontaminated water was applied to seeded pots during a six week period. Concentrations of water containing simazine levels of 0.0001. 0.01, 0.1 and 1.00 ppm were used. Visual injury and number of live seedlings were evaluated every seven days after the beginning of the treatments and a threshold concentration was determined. An immunoassay kit was evaluated for practicality to the golf industry. Species varied in their response to simazine concentrations and immunoassay diagnostic kits have potential for use in detecting phytotoxic simazine concentrations.