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農藥噴施過程中霧滴沉積分布與脫靶飄移研究
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國家自然科學基金項目(31371963)、江蘇省自然科學基金項目(BK20130965)、“十二五”國家科技支撐計劃項目〖JP2〗(2014BAD08B04)、江蘇省杰出青年教師培育聘專項目(2012256)、江蘇省青藍工程項目和江蘇高校優(yōu)勢學科建設工程項目


Droplet Deposition Distribution and Off-target Drift during Pesticide Spraying Operation
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    摘要:

    對農藥通過空氣運輸并沉積到靶標植物表面(葉片或其它部位)、地面(土壤表層)以及大氣(隨風飄移)等不同部分的沉積進行研究。以苦苣菜、棉花和稗草作為靶標植物,取其不同生長階段(總葉面積分別為15、135、300cm2)作為研究對象。在開路式風洞噴施加有熒光示蹤劑噴霧介質,通過清洗并分析植物葉片、地面上放置的聚酯薄膜卡和風洞中懸掛的聚乙烯線測定熒光劑含量,分析不同體積中徑、噴霧角、霧滴速度、流量、噴頭高度、風速、植物類型、生長階段等因素時的農藥霧化后的分配過程,定量測試不同參數對農藥在植物、地面和大氣中的沉積比例分配的影響。建立了基于跨幀技術的粒子圖像測速系統(tǒng)來增加測速范圍,包括激光成像系統(tǒng)、脈沖發(fā)生器和分析軟件。結果表明,噴霧角、霧滴速度、流量、植物類型等參數對植物、地面和大氣等不同部分農藥分配比例的影響不大,而霧滴粒徑、噴頭高度、風速、植物生長階段對植物、地面和大氣等不同部分農藥分配比例的影響顯著。當霧滴粒徑由445μm減小到181μm時,地面上的沉積比例由82.7%減少到57.7%,空氣中飄移部分的比例由30%減少到0.8%。當噴霧高度為40~60cm、風速2~4m/s時,農藥在植物上的沉積比例都達到13.4%以上。因此,噴施農藥時,應盡量使噴霧高度為40~60cm,風速小于4m/s,并根據防治目標、附近環(huán)境確定霧滴粒徑。當噴施土壤活性除草劑等農藥時,應選擇產生較大的霧滴粒徑,以增加在地面(土壤)上的沉積比例;而對于防治飛行類害蟲,農藥在空氣中飄移部分的比例可以提高防治效果,所以較小的霧滴更加有效。靶標植物本身的特性也會影響農藥的有效沉積效率,植物的生長階段越靠后,葉面積越大,農藥在植物上的沉積比例越高,在地面上沉積部分的比例越低,噴施除草劑時,盡量減少藥劑在單子葉作物葉片上的沉積,增加在雙子葉靶標雜草上的沉積量。選擇不同的參數,將導致植物上的藥劑有效沉積明顯不同,也會引起農藥流失部分的明顯不同。

    Abstract:

    Due to great human awareness of environmental conservation and public health, pesticides must be applied in economically viable and environmentally sensitive ways, and it requires deep understanding on the distributions of pesticide application. The distribution is the process occurring immediately after application. When applied, the pesticide can distribute in the following way: loss by wind drift, deposition on leaves or other parts of the target plant and deposition on ground (soil). The sum of these three components (plant, soil and drift) should equal to the amount of spray emitted. However, there are concerns over the intended effect (deposition on plant) and unintended effect (deposition on ground and wind drift) of pesticide application on the effectiveness and risks associated with the use of pesticides. Oriented to distribution of pesticide application, droplet deposition on different parts was measured in the research. Spray deposition was tested by recovery of a fluorescent tracer (pyranine) in the 1.75m wide, 1.75m high and 10m long working section of the wind tunnel. A single nozzle was positioned in the centre of the wind tunnel at a height of 0.6m above the wind tunnel floor and then sprayed moving along the length of the tunnel at a speed of 1m/s. The nozzle moved over the top of the plant so that application amount was the same to a typical spray in agriculture and the pesticide distribution was measured. Mylar cards (plastic) were used to collect the deposition on ground, diameter polythene lines were horizontally mounted to provide an estimate of the wind drift of spray, and the sow thistle plant was put under the nozzle to test the deposition on the target. To evaluate the influence of different factors on spray distribution, the trial was carried out for three plant types (sow thistle, cotton and barnyard grass) at three growth stages (leaf area were 15cm2, 135cm2 and 300cm2, respectively). After spraying, fluorescent dyes were easily washed off the three different samples so good recoveries can be got. The amount of spray on the plant, ground and wind drift was calculated and expressed as a percent (or fraction) of the amount of spray that came out of the nozzle. Based on the frame straddling technique, velocity of droplet was investigated by particle image velocimetry (PIV), and the test system included laser imaging system, pulse generator and analysis software. The influences of droplet size (VMD), droplet velocity, spray angle, flow rate, height of nozzle, wind speed and growth stage of plant on deposition at various parts were investigated. Correlation between different factors and spray distribution (fraction of spray deposited on ground, plant and drift) was calculated to judge the impact. The results indicated that the distribution of the spray was influenced by droplet size, release height wind speed and growth stage. Meanwhile, spray angle, sheet velocity flow rate and plant type had no significant effect on the spray distribution. The ground deposition was the lowest with the fine sprays. It was found that ground deposition from application of pesticides was 57.7% for finer droplet(VMD was 181μm) which was increased to 82.7% for coarser droplet (VMD was 445μm). Deposition on plant surfaces was also found to be more than 13.4% with release height at 40cm to 60cm and wind speed less than 4m/s. For soil-active herbicide, a proportion of deposit on the ground was increased by bigger VMD, and this is a desirable result. For controlling flying pest, airborne deposit can increase chemical’s spread on its body, so smaller VMD was more effective. It was also shown that the proportion of spray depositing on plant surfaces was increased as the plants got larger and the amount depositing on the ground was decreased. The result can be used to effectively aid spray decisions to maximize the effectiveness of pesticides and minimize risks to the environment from chemical spraying activities. Chemical application must be as precise as possible, so populations of unwanted organisms (insects or diseases) can be reduced and less environmental impacts created in the agricultural production. An understanding of the pesticide application process can be utilized to improve the estimate of the distribution on pesticide from a spray operation.

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張慧春,鄭加強,周宏平,DORR G J.農藥噴施過程中霧滴沉積分布與脫靶飄移研究[J].農業(yè)機械學報,2017,48(8):114-122. ZHANG Huichun, ZHENG Jiaqiang, ZHOU Hongping, DORR G J. Droplet Deposition Distribution and Off-target Drift during Pesticide Spraying Operation[J]. Transactions of the Chinese Society for Agricultural Machinery,2017,48(8):114-122.

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  • 收稿日期:2016-12-08
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  • 在線發(fā)布日期: 2017-08-10
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