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微咸水加肥灌溉下陶瓷灌水器与迷宫流道灌水器的抗堵塞性能
引用本文:王慧芸,陈俊英,王耀民,吴天奎,徐洋洋,张兴,陈慧芳,朱德兰,蔡耀辉.微咸水加肥灌溉下陶瓷灌水器与迷宫流道灌水器的抗堵塞性能[J].农业工程学报,2022,38(13):84-94.
作者姓名:王慧芸  陈俊英  王耀民  吴天奎  徐洋洋  张兴  陈慧芳  朱德兰  蔡耀辉
作者单位:1. 西北农林科技大学旱区农业水土工程教育部重点实验室,水利与建筑工程学院,杨凌 712100;;2. 武汉大学水利水电学院,武汉,430072;;3. 西北农林科技大学水土保持研究所,杨凌 712100;
基金项目:国家自然科学基金项目(52009113、51979234)
摘    要:为探求微孔陶瓷灌水器与迷宫流道灌水器在不同水质灌溉条件下抗堵塞性能的差异及堵塞机理,本研究选择了微咸水(A1)、肥水(A2)、微咸水加肥(A3)3种不同水质,分析管间式微孔陶瓷灌水器和6种常用的迷宫流道灌水器在不同水质灌溉条件下的平均相对流量变化规律,并用X射线衍射仪测定堵塞物质组成成分,用场发射扫描电镜观测堵塞物质表面微观形貌及动态生长过程。结果表明:各灌水器的流量随着灌溉运行时间的推移均发生不同程度的下降,其中A1处理下陶瓷灌水器的流量下降最慢,表现出优于迷宫流道灌水器的抗堵塞性能,A2、A3处理下陶瓷灌水器的平均相对流量下降速度先慢后快,试验结束时平均相对流量降幅最大,抗堵塞性能较差;A1处理下堵塞物质的主要成分是CaCO3,A2、A3处理下堵塞物质的主要成分是(NH4)2SO4;A1处理下各灌水器堵塞物表面微观形貌的生长过程为晶体颗粒不断团聚,A2、A3处理下堵塞物的动态生长过程为絮状物不断黏合成板块状或膜状。陶瓷灌水器堵塞发生在内壁上,堵塞物未进入到灌水器内部微孔中,随着堵塞物质增多且变得紧密复杂逐渐覆盖了内壁上的孔隙导致堵塞;迷宫流道灌水器是由于堵塞物质在流道内沉积导致过水断面减小,从而造成堵塞。研究结果可为陶瓷灌水器的应用及改进提供参考。

关 键 词:    灌水器  陶瓷  滴灌  微咸水
收稿时间:2022/1/26 0:00:00
修稿时间:2022/5/10 0:00:00

Anti-clogging performance of the ceramic emitters and labyrinth channel emitters under brackish water and fertilizer irrigation
Wang Huiyun,Chen Junying,Wang Yaomin,Wu Tiankui,Xu Yangyang,Zhang Xing,Chen Huifang,Zhu Delan,Cai Yaohui.Anti-clogging performance of the ceramic emitters and labyrinth channel emitters under brackish water and fertilizer irrigation[J].Transactions of the Chinese Society of Agricultural Engineering,2022,38(13):84-94.
Authors:Wang Huiyun  Chen Junying  Wang Yaomin  Wu Tiankui  Xu Yangyang  Zhang Xing  Chen Huifang  Zhu Delan  Cai Yaohui
Institution:1. Key Laboratory of Agricultural Soil and Water Engineering of Ministry of Education in Arid Regions, College of Hydraulic and Architectural Engineering ,Northwest A&F University, Yangling 712100, China;;2. College of Water Resources and Hydropower engineering, Wuhan university, Wuhan 430072, China;; 3. Institute of Soil and Water Conservation, Northwest A&F University, Yangling 712100, China;
Abstract:Seepage irrigation has been one of the most concerned irrigation technologies in recent years, due to its energy saving, high yield, and water use efficiency. However, the performance of ceramic emitter varies greatly under different water quality conditions. Particularly, there are various working modes in the ceramic emitter and conventional maze channel emitter. This study aims to explore the anti-clogging performance and clogging mechanism between the ceramic emitters and labyrinth channel emitters under different water quality irrigation conditions. The test platforms were also composed of the water storage bucket, electric pump whirlpool type self-priming electric pump, pressure gauge, mesh filter (125 microns), control valve, emitter, capillary, and return tank. The experiment was selected as saline water (A1), fertilizer water (A2), and saline water with fertilizer (A3). The ceramic emitters and six types of labyrinth channel emitters were selected for the continuous irrigation experiments. The Discharge Ratio Variation (Dra) was then monitored under different irrigation conditions of water quality. An X-ray Diffractometer (XRD) test was conducted to identify the clogging substance. A Scanning Electron Microscopy (SEM) was then utilized to characterize the surface morphology and growth process of the clogging substances. The results show that: 1) The excellent anti-clogging performance was achieved in the ceramic emitter under saline irrigation. The anti-clog time of the ceramic emitter was prolonged compared with the maze channel emitter. The chemical blockage was the main cause of the blockage, which was produced CaCO3 by chemical reactions of ions in brine. The chemical blockage was gradually reunited from the loose crystals to combine into the larger particles in the process of irrigation. Although the microhole was not completely covered in the inner wall of the ceramic emitter, the cross-section of labyrinth channels of the emitter was quickly reduced to plug the inner wall of the ceramic emitter rather than the pores. The tiny runner of the labyrinth channel emitters was then deposited to rapidly reduce the flow in the labyrinth channel emitter. 2) The ceramic emitter dropped rapidly at the high temperature and humidity under the fertilizer water irrigation, indicating the low clogging resistance on the whole. The blockage was mainly (NH4)2SO4 under the fertilizer water irrigation. That was because the proteins secreted by microorganisms were separated out in a highly saturated ammonium sulfate solution, and (NH4)2SO4 was wrapped in the protein and deposited on the inner wall of the emitter or in the flow channel. The blockage type was mainly a physical blockage, together with a biological blockage. Once the ceramic emitter flowed out from the inner wall, the precipitated protein flocculent cannot be discharged to deposit in the inner wall. As such, a dense layer of the membrane was formed on the inner wall. The very small microhole was fully clogged on the inner wall, resulting in the serious blockage of the ceramic emitter. The protein was suspended in the labyrinth channel emitters, then discharged with the water flow. Only a thin layer of membrane was attached to the runner wall, which was less impact on the area of the cross-section area. In addition, the ptfe tape was found to clog the water inlet in the labyrinth channel emitters, leading to a rapid early decline in the emitter flow. 3) The flow rate of ceramic emitter also decreased rapidly, when the temperature and humidity were higher under the saline water with the fertilizer irrigation. There was the most serious blockage at the end of the test, indicating a lower anti-blockage performance. The blockage was mainly (NH4)2SO4 Similar to fertilizer water irrigation, the physical blockage was dominated to accompany by biological blockage. The blockage process was also similar to fertilizer water irrigation. The dense membrane was formed on the inner wall of the ceramic emitter, where the flow rate decreased rapidly. At the same time, there was a thin blockage attached to the runner wall of the labyrinth channel emitters, where the flow rate decreased slowly. A large amount of EDTA chelator in the fertilizer was combined with the calcium and magnesium ions to form a chelation state soluble in water, which can effectively reduce the generation of chemical precipitation. The research results can also provide a theoretical basis to promote the anti-clogging performance of ceramic emitters.
Keywords:fertilizers  water  emitters  ceramic  drip irrigation  saline water
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