农业工程学报
農業工程學報
농업공정학보
2013年
14期
120-129
,共10页
商放泽%任树梅%邹添%杨培岭※
商放澤%任樹梅%鄒添%楊培嶺※
상방택%임수매%추첨%양배령※
土壤%入渗%蒸发%再生水%盐溶液%盐分%碱性
土壤%入滲%蒸髮%再生水%鹽溶液%鹽分%堿性
토양%입삼%증발%재생수%염용액%염분%감성
soils%infiltration%evaporation%treated wastewater%salt solutions%salinity%alkalization
为研究再生水利用对土壤盐碱性影响的特殊性,采用室内大型土槽试验,对比研究了清水、再生水和钠吸附比(sodium adsorption ratio,SAR)分别为3、10和20(mmolc/L)0.5的盐溶液入渗与蒸发10次(模拟灌溉2 a)期间对土壤及土壤溶液盐分迁移累积和碱性的影响。结果表明:与清水相比,再生水和SAR值为20(mmolc/L)0.5的盐溶液处理中0~40 cm 深度壤土含水率较高,80~120 cm 砂土含水率的增加产生滞后现象;再生水和盐溶液入渗与蒸发后土壤中盐分产生累积,累积量为9.54%~51.83%,而再生水处理中淋洗液带出的盐分最多,是其他处理的1.09~1.42倍。清水、再生水和盐溶液处理土壤溶液钠吸附比(SAR)<3(mmolc/L)0.5,土壤pH值<8.5,再生水和盐溶液入渗与蒸发引起土壤碱化的风险较低。再生水入渗与蒸发后土壤溶液中K+和Ca2+在土体中的迁移分布与清水和盐溶液处理不同,再生水对土壤中Cl-有较强的淋洗作用,长期再生水灌溉过程中土壤K+、Ca2+和Cl-的迁移和淋洗需要引起重视。试验结果对农业中长期安全合理利用再生水具有指导意义。
為研究再生水利用對土壤鹽堿性影響的特殊性,採用室內大型土槽試驗,對比研究瞭清水、再生水和鈉吸附比(sodium adsorption ratio,SAR)分彆為3、10和20(mmolc/L)0.5的鹽溶液入滲與蒸髮10次(模擬灌溉2 a)期間對土壤及土壤溶液鹽分遷移纍積和堿性的影響。結果錶明:與清水相比,再生水和SAR值為20(mmolc/L)0.5的鹽溶液處理中0~40 cm 深度壤土含水率較高,80~120 cm 砂土含水率的增加產生滯後現象;再生水和鹽溶液入滲與蒸髮後土壤中鹽分產生纍積,纍積量為9.54%~51.83%,而再生水處理中淋洗液帶齣的鹽分最多,是其他處理的1.09~1.42倍。清水、再生水和鹽溶液處理土壤溶液鈉吸附比(SAR)<3(mmolc/L)0.5,土壤pH值<8.5,再生水和鹽溶液入滲與蒸髮引起土壤堿化的風險較低。再生水入滲與蒸髮後土壤溶液中K+和Ca2+在土體中的遷移分佈與清水和鹽溶液處理不同,再生水對土壤中Cl-有較彊的淋洗作用,長期再生水灌溉過程中土壤K+、Ca2+和Cl-的遷移和淋洗需要引起重視。試驗結果對農業中長期安全閤理利用再生水具有指導意義。
위연구재생수이용대토양염감성영향적특수성,채용실내대형토조시험,대비연구료청수、재생수화납흡부비(sodium adsorption ratio,SAR)분별위3、10화20(mmolc/L)0.5적염용액입삼여증발10차(모의관개2 a)기간대토양급토양용액염분천이루적화감성적영향。결과표명:여청수상비,재생수화SAR치위20(mmolc/L)0.5적염용액처리중0~40 cm 심도양토함수솔교고,80~120 cm 사토함수솔적증가산생체후현상;재생수화염용액입삼여증발후토양중염분산생루적,루적량위9.54%~51.83%,이재생수처리중림세액대출적염분최다,시기타처리적1.09~1.42배。청수、재생수화염용액처리토양용액납흡부비(SAR)<3(mmolc/L)0.5,토양pH치<8.5,재생수화염용액입삼여증발인기토양감화적풍험교저。재생수입삼여증발후토양용액중K+화Ca2+재토체중적천이분포여청수화염용액처리불동,재생수대토양중Cl-유교강적림세작용,장기재생수관개과정중토양K+、Ca2+화Cl-적천이화림세수요인기중시。시험결과대농업중장기안전합리이용재생수구유지도의의。
In order to study the special effects of treated wastewater irrigation on soil salinize-alkalization, we built 5 large soil bins with length of 1.2 m, width of 1.2 m and height of 1.5 m, and filled with loam and sandy soil in 0~80 and 80-120 cm, respectively. Three infrared lamps and one electric fan were placed above the soil bin. After that, indoor large soil bins infiltration and evaporation experiments were conducted to research the effects of infiltration and evaporation with clear water, treated wastewater and salt solutions with SAR=3, 10 and 20 (mmolc/L)0.5 on soil, and soil solution salt and ions migration and accumulation, and soil alkalization. During the 10 times of infiltration and evaporation experiments (simulation field irrigation for 2 years), the electrical conductivity (EC), sodium adsorption ratio (SAR), pH, K+, Ca2+, Na+, Mg2+, Cl-, SO42-, and HCO3-in soil and soil solution were measured. The results showed that compared with the clear water irrigation, soil moisture in 0~40 cm loam were larger and the increasing of sandy soil moisture in 80-120 cm led to lagged effect. The reason was that the dissolved organic matter (DOM) and suspended solids in treated wastewater caused clay dispersion and blocked the soil pores, respectively,and Na+in treated wastewater and salt solutions with SAR=20 (mmolc/L)0.5 caused clay swelling and dispersion, during the infiltration and evaporation with treated wastewater and salt solution with SAR=20 (mmolc/L)0.5. The soil salt accumulated in treated wastewater and salt solutions treatments after 10 times of infiltration and evaporation, and the cumulant was between 9.54%and 51.83%, and the salt in leacheate was most in treated wastewater treatment, which was 1.09-1.42 times of other treatments. All treatments had similar effects on soil solution SAR value and soil pH, which were less than 3 (mmolc/L)0.5 and 8.5, respectively. The results showed a low possibility of soil alkalization during infiltration and evaporation with treated wastewater and salt solutions. As a coexistence system with variety of materials like salinity, nutrients, suspended solids and DOM, the mass concentrations of K+ and Ca2+ in soil solution showed a different distribution in various depths during infiltration and evaporation with treated wastewater. The mass concentration of Cl-in treated wastewater was about 0.3 times of salt solutions, but the mass concentration of Cl-in soil solution in treated wastewater treatment was 0.95-1.29 times of salt solutions treatments. The mass ratio of Cl-in soil also varied in different soil depths. The treated wastewater treatment had a stronger leaching ability on soil Cl-, and it may attribute to the particularity of treated wastewater and the results of soil maintain charge balance. According to the results, it was concluded that compared with clear water and salt solutions, soil salinity and some salt ions indicated a different migration and distribution in the soil profile after infiltration and evaporation with treated wastewater, and more attention should be paid to the migration and leaching of K+, Ca2+and Cl-. The results of this research provide references for the long-term secure and rational irrigation with treated wastewater in agriculture.