Academic literature on the topic 'Endothall (Herbicide)'

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Journal articles on the topic "Endothall (Herbicide)"

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Barua, Rajesh, Peter Boutsalis, Jenna Malone, Gurjeet Gill, and Christopher Preston. "Incidence of multiple herbicide resistance in annual bluegrass (Poa annua) across southeastern Australia." Weed Science 68, no. 4 (2020): 340–47. http://dx.doi.org/10.1017/wsc.2020.35.

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AbstractAnnual bluegrass (Poa annua L.) is a problematic annual weed in established turf where the intensive use of herbicides has resulted in the evolution of herbicide resistance. In 2017, 31 populations of P. annua suspected to be resistant to herbicides commonly used to control this weed in turf were collected from golf courses across southeastern Australia to check the resistance status to different herbicide groups. All populations were found to be resistant to multiple turf herbicides. Dose–response experiments confirmed resistance to propyzamide, simazine, rimsulfuron, foramsulfuron, e
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Islam, Md Shahidul, Trevor D. Hunt, Zhiqian Liu, Kym L. Butler, and Tony M. Dugdale. "Sediment Facilitates Microbial Degradation of the Herbicides Endothall Monoamine Salt and Endothall Dipotassium Salt in an Aquatic Environment." International Journal of Environmental Research and Public Health 15, no. 10 (2018): 2255. http://dx.doi.org/10.3390/ijerph15102255.

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Endothall dipotassium salt and monoamine salt are herbicide formulations used for controlling submerged aquatic macrophytes and algae in aquatic ecosystems. Microbial activity is the primary degradation pathway for endothall. To better understand what influences endothall degradation, we conducted a mesocosm experiment to (1) evaluate the effects of different water and sediment sources on degradation, and (2) determine if degradation was faster in the presence of a microbial community previously exposed to endothall. Endothall residues were determined with LC-MS at intervals to 21 days after e
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Johnson, W. C., D. L. Colvin, T. A. Littlefield, and B. G. Mullinix. "Florida Beggarweed (Desmodium tortuosum) and Sicklepod (Senna obtusifolia) Control in Peanut Using Herbicides Applied Through a Wick-Bar1." Peanut Science 26, no. 1 (1999): 18–23. http://dx.doi.org/10.3146/i0095-3679-26-1-5.

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Abstract Tall weeds in peanut fields cause losses other that yield reduction from competition by intercepting fungicides and insecticides, and interfering with harvest efficiency. Studies were conducted at Archer, FL and Tifton, GA in 1994 and 1995 to determine an effective means to selectively control tall Florida beggarweed and sicklepod late season in peanut using herbicides applied with a wickbar. Herbicides evaluated were glyphosate, paraquat, and dimethylalkylamine salt of endothall (DMAA endothall); each applied at 0, 25, 50, 75, and 100% by volume. Treatments were applied in two passes
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Williams, Max W., Sally A. Bound, Jack Hughes, and Stuart Tustin. "183 ENDOTHALL, A BLOSSOM-THINNING AGENT FOR APPLES." HortScience 29, no. 5 (1994): 455c—455. http://dx.doi.org/10.21273/hortsci.29.5.455c.

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Endothall [7, oxybicyclo (2,2,2) heptane-2-3 dicarboxylic acid] is an aquatic herbicide which has potential for use as a blossom thinning agent for apples. Trials conducted in Washington State, New Zealand and Australia on several apple cultivars indicate Endothall is a safe, consistent blossom thinner. Cultivars treated were `Golden Delicious', `Delicious', and `Gala'. Single and repeat applications were used in the New Zealand tests. With multiple applications of Endothall, no fruit marking occurred on any of the test cultivars. In temperate fruit zones with extended apple bloom periods, mul
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Williams, Max W., Sally A. Bound, Jack Hughes, and Stuart Tustin. "Endothall: A Blossom Thinner for Apples." HortTechnology 5, no. 3 (1995): 257–59. http://dx.doi.org/10.21273/horttech.5.3.257.

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Endothall [7, oxabicyclo (2,2,1) heptane-2-3 dicarboxylic acid] is an aquatic herbicide with potential use as a blossom thinner for apples (Malus domestics Borkh.). Trials conducted in Washington, New Zealand, and Australia on several apple cultivars indicate that endothall is a safe, consistent blossom thinner. Cultivars treated were `Golden Delicious', `Delicious', `Royal Gala', and `Granny Smith'. Single and repeat applications were used in the New Zealand and Washington tests. With multiple applications of endothall, no fruit marking occurred on any of the test cultivars. In temperate frui
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Wersal, Ryan M., and John D. Madsen. "Comparison of Subsurface and Foliar Herbicide Applications for Control of Parrotfeather (Myriophyllum aquaticum)." Invasive Plant Science and Management 3, no. 3 (2010): 262–67. http://dx.doi.org/10.1614/ipsm-d-09-00058.1.

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AbstractParrotfeather is an invasive, aquatic plant in the United States that is native to South America. It has impaired the use of water bodies throughout the United States and is difficult to control, despite using a variety of management techniques. Our objectives were to examine the efficacy of subsurface applications of seven herbicides labeled for aquatic use and to compare those applications to herbicides that can also be applied to emergent foliage. A replicated mesocosm study was conducted in 378-L (100-gal) tanks beginning in August 2007 and repeated during the same period in 2008.
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Koschnick, Tyler J., William T. Haller, and Greg E. MacDonald. "Turf and Ornamental Plant Tolerances to Endothall in Irrigation Water I. Ornamental Species." HortTechnology 15, no. 2 (2005): 318–23. http://dx.doi.org/10.21273/horttech.15.2.0318.

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Restrictions on the endothall aquatic herbicide label include the use of endothall treated water for irrigating plants from 7 to 25 days after application. This interval was established to allow sufficient time for endothall to dissipate to levels that were considered safe for irrigation to prevent phytotoxicity to desirable plants. The affects of endothall on begonias (Begonia semperflorens `Vodka Cocktail'), pansies (Viola × wittrockiana `Atlas Purple'), petunias (Petunia hybrida), and impatiens (Impatiens wallerana `Lipstick') were determined by comparing aboveground dry weight to control p
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Reinert, Kevin H., Susan Stewart, Mark L. Hinman, John H. Rodgers, and Tim J. Leslie. "Release of endothall from aquathol granular aquatic herbicide." Water Research 19, no. 6 (1985): 805–8. http://dx.doi.org/10.1016/0043-1354(85)90130-7.

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Bultemeier, Brett W., Mike D. Netherland, Jason A. Ferrell, and William T. Haller. "Differential Herbicide Response among Three Phenotypes ofCabomba caroliniana." Invasive Plant Science and Management 2, no. 4 (2009): 352–59. http://dx.doi.org/10.1614/ipsm-09-035.1.

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AbstractCabomba is a submersed aquatic plant native to the southeastern United States that is commonly sold worldwide through the aquarium trade. While infrequently managed in its native range, cabomba has recently been reported as invasive and tolerant to management efforts in the northern areas of the United States and in other countries. Invasive populations of cabomba are characterized by a phenotype that is bright green. In contrast, cabomba native to the southeastern United States is characterized by a red phenotype, while plants sold through the aquarium trade have intermediate characte
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Koschnick, Tyler J., William T. Haller, and Alison M. Fox. "Turf and Ornamental Plant Tolerances to Endothall in Irrigation Water II. Turf Species." HortTechnology 15, no. 2 (2005): 324–29. http://dx.doi.org/10.21273/horttech.15.2.0324.

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Two formulations of the contact herbicide endothall are used to control submersed aquatic weeds. Waters treated with the amine or dipotassium salt formulations have irrigation restrictions varying from 7 to 25 days depending on the concentration of endothall applied. These water-use restrictions may be reduced for turfgrass if studies conclude there is no phytotoxicity to turf species irrigated with concentrations of endothall that may exist after an aquatic application. Two separate experiments were conducted to determine turfgrass tolerance to endothall in irrigation water on five species of
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Books on the topic "Endothall (Herbicide)"

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Getsinger, Kurt D. Evaluation of endothall/adjuvant mixtures in flowing water. U.S. Army Engineer Waterways Experiment Station, 1988.

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Book chapters on the topic "Endothall (Herbicide)"

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"Balancing Fisheries Management and Water Uses for Impounded River Systems." In Balancing Fisheries Management and Water Uses for Impounded River Systems, edited by Michael D. Netherland. American Fisheries Society, 2008. http://dx.doi.org/10.47886/9781934874066.ch32.

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<em>Abstract</em>.—Herbicide use to control aquatic vegetation in southern reservoirs can elicit a wide range of responses and concerns from the fishing community, lake property owners, and the general public. Debates regarding the need to control aquatic plants, how much vegetation to control and where, and the herbicides chosen can be divisive. This paper will focus on the use patterns and technical features of aquatic herbicides and factors that should be considered when implementing a herbicide program for aquatic plant management in reservoirs. Both the angling community and general public often have misconceptions regarding herbicide use patterns, plant selectivity and nontarget impacts, and management objectives. There are currently 10 herbicide active ingredients registered for aquatic use. Glyphosate and imazapyr are used strictly for emergent aquatic plant control while copper, endothall, and fluridone are used almost exclusively for submersed plant control. The herbicides diquat, carfentrazone, penoxsulam, triclopyr, and 2,4-D are used for both emergent and submersed plant control. Many of the registered herbicides have been used since the 1950s and 1960s for aquatic plant management. Each compound has unique properties that impact the recommended use rates and use patterns, label restrictions, and plant selectivity. There are also several new herbicides that are currently being evaluated for aquatic plants. While herbicides are used in a wide variety of aquatic systems, reservoirs often present unique challenges due to high-flow events and vegetation growing in narrow strips along the shoreline or in open flats. Rapid dilution or dispersion of the herbicide from the target area remains a significant technical challenge in reservoirs. The introduction of invasive plants such as hydrilla <em>Hydrilla verticillata </em>and Eurasian watermilfoil <em>Myriophyllum spicatum </em>has increased the complexity of management decisions. These fast-growing submersed species can be viewed as both beneficial and detrimental to various reservoir systems. While some see these plants as invasive species that require management, others see them as providing valuable habitat in systems with limited native vegetation. Despite both social and environmental challenges, aquatic herbicides continue to provide reliable, relatively rapid results and site-specific aquatic plant management at a wide variety of scales.
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Manzoor, Javid, Manoj Sharma, Irfan Rashid Sofi, Mufida Fayaz, and Musadiq Hussain Bhat. "Status of Indian Wetlands With Special Reference to Pesticides and Their Impact." In Advances in Environmental Engineering and Green Technologies. IGI Global, 2019. http://dx.doi.org/10.4018/978-1-5225-6111-8.ch004.

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Wetlands are home to numerous species of fish, birds, and reptiles. The enormous roots of the mangrove trees act as shelter to small fish, reptiles, and amphibians. Pesticides and agro-chemical fertilizers have been playing a very pivotal role in the degradation of the land and the water bodies. The different herbicides that are present in wetlands are Dicamba, Endothall, MCPA, Triallate, Trifluralin, 2, 4-D, and insecticides Carbaryl, Carbofuran, Fenvalerate, Malathion, Parathion, and Terbufos. These pesticides have been provided with the aim of catering to the security of the crops which are highly vulnerable to the pests. However, harmful effects of pesticides on wetland species have been a concern for long time. Wetlands constitute one such habitat threatened by the pesticides. But there has been a lack of comprehensive research in this direction. The chapter will identify the gaps in the current research and will review the status of Indian wetlands with special reference to pesticides and their impact.
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"of control. The state of Queensland has generous expertise in this area, with the CSIRO Division of Entomology – Lands Department group in Brisbane boasting spectacular success against Salvinia and Eichhornia, and near the reservoir at James Cook University a USDA unit was involved in successes with the Tennessee Valley Authority (TVA) (see Chapter 12) using a range of stem-boring and leaf-mining insects (Balciunas et al. 1993). One might consider the herbivorous grass carp Ctenopharyngodon idella, originally from China, more as a harvester than a biological control agent. This fish grazes on submerged weeds such as Hydrilla, Myriophyllum, Chara, Potamogeton and Ceratophyllum, and at stocking rates of 75 fish/ha control is rapidly achieved. Some introductions in the USA have resulted in removal of all vegetation (Leslie et al. 1987), and in the Australian context the use of sterile (triploid) fish (Cassani and Canton 1985) could be the only consideration. However, in view of the damage already done by grass carp to some inland waterways in Australia, it is suspected that this option would be greeted with horror. Mechanical control involves the physical removal of weeds from a problem area and is useful in situations where the use of herbicides is not practical or poses risks to human health or the environment. Mobile harvesters sever, lift and carry plants to the shore. Most are intended for harvesting submerged plants, though some have been designed or adapted to harvest floating plants. Handling the harvested weed is a problem because of their enormous water content, therefore choppers are often incorporated into harvesting machinery design. However, many mechanical harvesters have a small capacity and the process of disposing of harvested plant material is time-consuming. Any material that remains may affect water quality during the decay process by depleting the water of oxygen. Furthermore, nutrients released by decay may cause algal blooms (Mitchell 1978). Another disadvantage of mechanical removal is that disturbance often promotes rapid new growth and germination of seed, and encourages the spread of weed by fragmentation. Some direct uses of macrophytes include the following: livestock food; protein extraction; manufacture of yeast; production of alcohol and other by-products; the formation of composts, mulches and fertilizers; and use for methane generation (Williams 1977). Herbicides either kill on contact, or after translocation through the plant. Some are residual and retain their toxicity for a period of time. Where herbicides are used for control of plants, some contamination of the water is inevitable (Bill 1977). The degree of contamination depends on the toxicity of the material, its fate and persistence in the water, the concentration used and the main purpose served by the water. After chemical defoliation of aquatic vegetation, the masses of decaying organic debris produced can interfere with fish production. Several factors must be taken into account when selecting and adapting herbicides for aquatic purposes, including: type of water use; toxicity of the herbicide to humans, fish, stock, and wildlife; rate of disappearance of residues, species affected and duration of control; concentration of herbicide; and cost (Bill 1977). The TVA has successfully used EPA-approved herbicides such as Endothall, Diquat, Fluridone and Komeen against Hydrilla (Burns et al. 1992), and a list of approved." In Water Resources. CRC Press, 1998. http://dx.doi.org/10.4324/9780203027851-40.

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Reports on the topic "Endothall (Herbicide)"

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Pokrzywinski, Kaytee, West Bishop, Christopher Grasso, Kaitlin Volk, and Kurt Getsinger. Chemical management strategies for starry stonewort : a mesocosm study. Engineer Research and Development Center (U.S.), 2021. http://dx.doi.org/10.21079/11681/42040.

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US Environmental Protection Agency (USEPA) approved algaecides and herbicides are frequently utilized to manage nuisance algae and aquatic macrophytes. However, there is limited information available on the effectiveness of these products for the management of starry stonewort. Thus, the goal of this research was to discern effective chemical control products for later growth stages of starry stonewort using mesocosm studies. Eleven treatments were evaluated using various combinations of four copper-based products, endothall, diquat, and carfentrazone – all with USEPA registrations for use in
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