植物营养与肥料学报
植物營養與肥料學報
식물영양여비료학보
PLANT NUTRITION AND FERTILIZER SCIENCE
2010年
1期
99-104
,共6页
直播稻田%铵态氮%硝态氮%渗漏量%太湖地区
直播稻田%銨態氮%硝態氮%滲漏量%太湖地區
직파도전%안태담%초태담%삼루량%태호지구
direct-seeding rice paddy%ammonium-nitrogen%nitrate-nitrogen%leaching flux%Taihu Lake Basin
在太湖流域丹阳地区,通过田间试验研究了旱直播稻田氮素的渗漏损失特征.结果表明,在当地正常的水肥管理模式下,旱直播稻田氮素的渗漏主要发生在水稻生长前期,施入的基肥不易迅速水解,部分仍滞留在表层土壤,灌溉或强降水时增大了氮素渗漏流失的风险.稻田40 cm深度土壤硝态氮和铵态氮浓度平均值分别为5.79和0.49 mg/L,硝态氮浓度最大值出现存苗肥施入后的第7 d,达到21.8 mg/L.以土壤深度40 cm为界面计算的氮素渗漏通量表明,铵态氮和硝态氮在整个稻季的平均渗漏量为N 3.8和28.4 kg/hm~2,氮素渗漏的形式主要为硝态氮.直播水稻萌芽至幼苗期对氮素的吸收量少,应适当减少前期基肥或苗肥的施用量,充分利用基肥与苗肥的叠加效应,减少前期氮素渗漏流失.
在太湖流域丹暘地區,通過田間試驗研究瞭旱直播稻田氮素的滲漏損失特徵.結果錶明,在噹地正常的水肥管理模式下,旱直播稻田氮素的滲漏主要髮生在水稻生長前期,施入的基肥不易迅速水解,部分仍滯留在錶層土壤,灌溉或彊降水時增大瞭氮素滲漏流失的風險.稻田40 cm深度土壤硝態氮和銨態氮濃度平均值分彆為5.79和0.49 mg/L,硝態氮濃度最大值齣現存苗肥施入後的第7 d,達到21.8 mg/L.以土壤深度40 cm為界麵計算的氮素滲漏通量錶明,銨態氮和硝態氮在整箇稻季的平均滲漏量為N 3.8和28.4 kg/hm~2,氮素滲漏的形式主要為硝態氮.直播水稻萌芽至幼苗期對氮素的吸收量少,應適噹減少前期基肥或苗肥的施用量,充分利用基肥與苗肥的疊加效應,減少前期氮素滲漏流失.
재태호류역단양지구,통과전간시험연구료한직파도전담소적삼루손실특정.결과표명,재당지정상적수비관리모식하,한직파도전담소적삼루주요발생재수도생장전기,시입적기비불역신속수해,부분잉체류재표층토양,관개혹강강수시증대료담소삼루류실적풍험.도전40 cm심도토양초태담화안태담농도평균치분별위5.79화0.49 mg/L,초태담농도최대치출현존묘비시입후적제7 d,체도21.8 mg/L.이토양심도40 cm위계면계산적담소삼루통량표명,안태담화초태담재정개도계적평균삼루량위N 3.8화28.4 kg/hm~2,담소삼루적형식주요위초태담.직파수도맹아지유묘기대담소적흡수량소,응괄당감소전기기비혹묘비적시용량,충분이용기비여묘비적첩가효응,감소전기담소삼루류실.
Field experiment of nitrogen leaching loss in a dry direct-seeding rice paddy was conducted in Danyang region of Taihu Lake Basin. Results show that the nitrogen leaching loss is mainly occurred during the early stage of rice growing season under local water and fertilizer management, especially for the seedling fertilization. The base fertilization has not rapidly hydrolyzed without standing water in about two weeks after rice is sowed, that resulted in part of the fertilizers still exists in surface soil. Even though part of the base fertilizers is transformed into nitrate-nitrogen in wet soil, the nitrate nitrogen still resides in surface soil without downward water-leaching. Both the residual base fertilizers and the added seedling fertilizers increase the chance of nitrogen leaching loss when irrigation or precipitation occurred. The mean concentrations of ammonia-nitrogen and nitrate-nitrogen, at 40 cm soil depth, are 5.79 and 0.49 mg/L respectively, and nitrate-nitrogen is the main part of nitrogen loss through leaching, whose maximal concentration is 21.8 mg/L on day 7 after the seedling fertilization. The mean quantities of leaching loss of ammonia-nitrogen and nitrate-nitrogen at soil depth of 40 cm, in the whole rice growing season, are about N 3.8 and 28.4 kg/ha respectively, which indicate that the nitrate-nitrogen accounts for a majority proportion. As a result, in direct-seeding rice paddies, the superposition effect of both base and seedling fertilizers should be paid more attention. Due to the low nitrogen-uptake of rice at its seedling stage, the prophase fertilizers may be advisably reduced to decrease the risk of nitrogen leaching.