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稻田     
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  paddy field
     α BHC,β BHC,δ BHC, γ BHC, p,p' DDE, p,p' DDD, p,p' DDT, o,p' DDT ranged from 7 5 to 71 1 ng/g in wastewater irrigated vegetable and maize field and from 3 0 to 16 5ng/g in wastewater irrigated paddy field.
     结果表明 ,α BHC、β BHC、δ BHC、γ BHC、p ,p’ DDE、p ,p’ DDD、p ,p’ DDT、o ,p’ DDT的检出率为 1 0 0 % ,这些有机氯农药在污灌旱地和稻田地的残留量分别为 7 5~ 71 1ng/ g和 3 0~ 1 6 5ng/ g .
短句来源
     Primary Analysis in the Effects of Elevated[CO_2] on Emission of CO_2 from Rice Paddy Field
     高CO_2浓度对稻田CO_2排放影响的初步分析
短句来源
     Weed Control in Paddy Field by IR5878
     IR5878防除移栽稻田杂草试验
短句来源
     The trial of soil conditioner Mianshengeng, with the applications of 3000g, 3750g, and 4500 g / hm 2, in paddy field for no tillage rice cultivation was carried out. The results showed that compared to the check, the treatment significantly out yielded by 967.5 to 1237.5 kg / hm 2 , of which the most obvious efficiency was the application of 3750 g / hm 2 with 2.67 of output / input ratio.
     应用土壤调理剂“免深耕”3000、3750和4500g/hm2在稻田上进行免耕效应试验,结果显示,施用不同用量的“免深耕”比对照增产稻谷967.5~1237.5kg/hm2,增产极显著,以3750g/hm2的用量处理增产效果最好,产投比达2.67。
短句来源
     EFFECT OF SOIL WATER REGIME AND SOIL TEXTURE ON N_2O EMISSION FROM RICE PADDY FIELD
     土壤水分状况和质地对稻田N_2O排放的影响
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  rice field
     Experiment of Rice Field Culture of Monopterus alba (Zuiew)
     黄鳝Monopterus alba(Zuiew)稻田养殖(Rice Field Culture)试验
短句来源
     The emission of CH_4 and N_2O in aerobic rice field mulched with straw.
     覆草旱作稻田CH_4和N_2O的排放
短句来源
     CH_4 and N_2O emissions from phaeozem rice field and their mitigative measures
     黑土稻田CH_4与N_2O排放及减排措施研究
短句来源
     CH_4 and N_2O emission from a rice field and effect of Azolla and fertilitaion on them
     稻田CH_4和N_2O的排放及养萍和施肥的影响
短句来源
     4. In the range of pH5-5.8 and pH6.2-6.8, CH4 flux from rice field increasing with the soil pH,there is a linear relationship between CH4 flux and soil pH.
     4.土壤pH6.2-6.8和5-5.8范围内,稻田CH_4排放随着pH的升高而增加,两者呈显著的正相关关系。
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  paddy
     Studies on Urease in Red Soil Paddy Fields
     红壤稻田脲酶研究
短句来源
     Ecological Risk Assessment of Bt Rice on Arthropod Community and Dominant Natural Enemies in Rice Paddy Habitat
     Bt水稻对稻田节肢动物群落和优势天敌的生态风险评价
短句来源
     Study on N_2O Emissions and Nitrogen Transformation in Leaching Solution in Cracking Paddy Soils
     裂缝条件下稻田土壤中N_2O的释放和氮溶质运移的机理研究
短句来源
     Nitrogen Originating from Environment in Paddy Ecosystem under Anthropogenic Influences
     人为影响下稻田生态系统环境来源氮解析
短句来源
     A PRELIMINARY STUDY ON SPIDERS FROM THE PADDY FIELDS IN ANHWEI PROVINCE
     安徽稻田蜘蛛初步研究
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  rice fields
     The level of ammonium nitrogen ranged from 0.36mg/L to 0.56mg/L, and the nitrate nitrogen altered in the range from 0.4mg/L to 0.8mg/L in the rice fields.
     试验前后稻田中的氨态氮(0.36mg/L-0.56mg/L)和硝态氮(0.4mg/L-0.8mg/L)变化不大。
短句来源
     CH_4 and N_2O fluxes from late rice fields in Guangzhou region and their affecting factors.
     广州地区晚稻田CH_4和N_2O的排放通量及其影响因素
短句来源
     Influence of nitrogen and phosphorus fertilizers on N_2O emissions in rice fields
     氮肥和磷肥对稻田N_2O排放的影响
短句来源
     while the loss of dimethoate via drainage and leakage was 238.5 and 160.8 g·hm~(-2),respectively,forming a total loss percentage of about 13.4% from the rice fields.
     乐果的稻田排水流失量为238.5g·hm-2,渗漏流失量为160.8g·hm-2,总流失量为其稻季用量的13.4%。
短句来源
     Evaluation of 50% YRC2388 WP Herbicidal Efficacy in Direct-seeded Rice Fields
     50%YRC2388 WP防除水直播稻田杂草效果评价
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  paddy field
Off-line experiments have been conducted with IAP94 land surface model on different surface types (cropland, forest and paddy field) in different seasons (spring, summer and autumn) over the Huaihe River basin.
      
Pronounced concentration-dissipation law of total function score value occurs in paddy field units, with three ranges, i.e., 79~68.5, 68.5~59 and 59~51.
      
Paddy field quality is divided into three gradations, and the scales are 18 220.9 ha, 5410.6 ha and 2890.9 ha.
      
A 21-day laboratory incubation experiment was conducted to investigate the impact of pesticides (insecticide, herbicide, fungicide) on paddy field soil health under controlled moisture (flooded soil) and temperature (25°C) environment.
      
N2O emission from paddy field under different rice planting modes
      
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  rice field
In the rice field methane is produced in the soil layer with depths of 2-25 cm.
      
The degradation of pencycuron in waterlogged tropic rice field was investigated.
      
To determine oogenesis in first-generation females (summer females) and its relations to temperature, females were collected from a rice field in early and mid-July and reared on young rice plants at 28, 31 and 34°C in the laboratory.
      
Carp of about 150 mm body length were released in small plots set in a rice field in southern Japan at 0, 0.2, or 0.6 carp/m2.
      
In the present study, we examined the role of leucine-enkephalin on moulting and vitellogenesis of the fresh water rice field crab, Oziotelphusa senex senex.
      
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  paddy
The Eh of the surface horizons of the paddy soils under the field conditions were +40, -12, -84, and -122 mV, respectively, while the Eh in the nonpaddy soils were close to +90 mV.
      
The amounts of organic matter and available Fe, Mn, Zn, and Cu increased, while the available K decreased in the paddy soils.
      
Six paddy soils, chosen so as to have different organic carbon contents, were experimented in this investigation.
      
For example, the average content of Zn in vegetable garden soils was 2.5-4 times as much as in their originated soils, and was lower in paddy soils than in their originated soils.
      
The vertical profile of methane production rate in the paddy soil during the water covering period differs from that in the paddy soil in dry phase.
      
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  rice fields
This further indicates that a sequence of different land uses including flooded rice fields is an important factor determining N outflow in basins in Japan.
      
Model for methane emission from rice fields and its application in southern china
      
The model has been used to calculate the methane emission from rice fields.
      
The influence of climate conditions, field water management, organic fertilizers and soil types on methane emission from rice fields are considered.
      
Soil organic matter content and soil physics and chemistry are major factors that determine the total season average emission rate, while soil temperature controls the temporal variation of methane emission from rice fields.
      
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