绿黄隆在麦茬土壤中的残留及其对后茬水稻的影响

应用核素示踪技术，以＾１４Ｃ－绿黄隆进行麦茬土壤残留及其后茬水稻影响的盆栽试验研究。结果表明，施地麦地的绿黄隆经过麦季（２０６ｄ）后有２５－３０％残留土壤；经过－稻两季（３２６ｄ）仍有约１５％的绿黄隆残留在土壤中，麦茬土壤中残留的绿黄隆晋茬水稻根系生长，而影响植株的生长发育；水稻植株残留量和转移系数是根系〉〉茎叶〉稻谷，在各部位的分布是不均匀的。     

江苏省主要水稻品种对甲磺隆的敏感性研究

在用土培方法探索水稻土培生物测定条件的基础上，研究了甲磺隆残留对水稻秧苗根系生长的影响。结果表明，采用高沙土，添加法加入甲磺隆，培养时调节土壤含水量３５％左右，恒温培养６ｄ，将获得满意的甲磺隆残留土培生物测定结果；用此方法测得的江苏主要水稻品种对甲磺隆残留的敏感程度呈现：常规粳稻＞糯稻、杂交粳稻＞常规籼稻＞杂交籼稻之趋势；土壤中甲磺隆残留量达０５μｇ／ｋｇ对江苏大多数水稻品种秧苗根系生长有着强烈的抑制作用。     

绿磺隆在土壤中的残留及其对后茬作物的安全性

研究了绿磺隆在江苏省吴县及河北省石家庄市麦田土壤中的降解规律 ,以及水稻对绿磺隆的敏感性。结果表明 ,绿磺隆在土壤中残留期较长 ,在江苏省吴县及河北省石家庄市麦田土壤中的降解半衰期分别为 2 2 82和 3 2 98d ;水稻对绿磺隆极为敏感 ,它对水稻根系生长的抑制浓度仅为 0 1 μg/kg,麦收后土壤中残留的绿磺隆极易对后茬水稻产生危害。     

绿磺隆在土壤中的残留及其对后茬作物的安全性

研究了绿磺隆在江苏省吴县及河北省石家庄市麦田土壤中的降解规律,以及水稻对绿磺隆的敏感性。结果表明,绿磺隆在土壤中残留期较长,在江苏省吴县及河北省石家庄市麦田土壤中的降解半衰期分别为22．82和32．98d;水稻对绿磺隆及敏感,它对水稻根系生长的抑制浓度仅为0．1μg/kg,麦收后土壤中残留的绿磺隆极易对后茬水稻产生危害。     

绿磺隆在土壤中的残留与危害

江苏省苏南地区，冬季麦田每公顷施用１５ｇ绿磺隆（以有效成份计，下同），翌年水稻栽秧时土壤中绿磺隆的残留量为０．２２μｇ／ｋｇ，种麦期间绿磺隆在土壤中的降解量约占施用量的９６．８％，绿磺隆在土壤中的降解半衰期平均为３８．６ｄ。水稻对绿磺隆也有高度的敏感性，由于绿磺隆在渍水土壤中容易降解，所以它在稻麦轮作地区对后茬水稻的实际危害较轻。改善土壤肥力状况，在一定程度上可减缓绿磺隆对作物的危害。     

绿磺隆在土壤中的残留与危害

江苏省苏南地区，冬季麦田每公顷施用１５ｇ绿磺隆（以有效成份计，下同），翌年水稻栽秧时土壤中绿磺隆的残留量为０．２２μｇ／ｋｇ，种麦期间绿磺隆在土壤中的降解量约占施用量的９６．８％，绿磺隆在土壤中的降解半衰期平均为３８．６ｄ。水稻对绿磺隆也有高度的敏感性，由于绿磺隆在渍水土镶中容易降解，所以它在稻麦轮作地区对后茬水稻的实际危害较轻。改善土壤肥力状况，在一定程度上可减缓绿磺隆对作物的危害。     

江苏省主要水稻品种对甲磺隆的敏感性研究

在用土培方法探索水稻土墙玫瑰测定条件的基础上，研究了甲磺隆残留对水稻秧苗根系生长的影响。结果表明，采用高沙土、添加法加入甲磺隆，培养时调节含水量３５％左右，恒温ｄ，将获得满意的甲磺隆残留土培生物测定结果；用此方法测得的江苏主要水稻品种对甲磺隆残留的敏感程度呈现：常规粳稻，糯稻、杂交粳稻〉常规灿稻〉杂交灿稻之趋势；土壤中甲磺隆残留量达０．５μ／ｋｇ对在多数水稻品种秧苗根系生长有着强烈的抑制作用。     

绿磺隆残留对水稻生长的影响

观察了不同水稻品种对绿磺隆的敏感性，发现“９３２５”、“９－９２”、“９３８０”等３品种对绿黄隆高度敏感。采用添加法试验，证实绿磺隆残留对水稻株高、分蘖、干物质积累、产量影响明显，残留致使“９－９２”水稻减产２．３２％～２３．５８％。建议在镇江市沿江、孟河平原和丘陵非重草害田块，应停止使用绿磺隆或通过复配方式，降低绿磺隆用量。     

绿磺隆残留对水稻生长的影响

观察了不同水稻品种对绿磺隆的敏感性，发现“９３２５”、“９－９２”、“９３８０”等３品种对绿黄隆高度敏感。采用添加法试验，证实绿磺隆残留对水稻株高、分蘖、干物质积累、产量影响明显，残留致使“９－９２”水稻减产２．３２％￣２３．５８％。建议在镇江市沿江、孟河平原和丘陵非重草害田块，应停止使用绿磺隆或通过复配方式，降低绿磺隆用量。     

绿磺隆对水稻的残留危害剂量

用田间模拟试验法，研究了土壤中绿磺隆不同添加量与水稻危害剂量的关系。结果表明：稻田绿磺隆添加量超过０．３７５ｇ（ＡＩ）／ｈｍ￣２时，就可能对水用产生危害，在此用量水平下，绿磺隆在耕层土壤中的平均残留浓度为０．１７μｇ／ｋｇ，按此推算，麦田按正常用量的２倍量（３０ｇ／ｈｍ￣２）施用，在种麦期间绿磺隆在麦田土壤中的半衰期超过３２．１ｄ．即会对水稻产生危害。     

水稻田烤田期间甲烷排放规律研究

报道了在镇江丘陵区水稻生产中的烤田期间不同处理的甲烷排放特点及其与土壤水分、氧化还原电位的关系。结果表明,在烤田初期有一个甲烷排放高峰,然后很快下降,烤田后期甲烷排放接近于零;前茬施用稻草,对烤田期间甲烷排放有显著的促进作用;不同氮肥用量对甲烷排放的影响规律不明显;烤田期间甲烷排放占水稻全生育期排放量的比例,在３．８６％～１３．９２％范围内变化。     

Case study on nitrogen and phosphorus emissions from paddy field in Taihu region

The agricultural non-point source pollution by nitrogen (N) and phosphorus (P) loss from typical paddy soil (whitish soil, Bai Tu in Chinese) in the Taihu Lake region was investigated through a case study. Results shown that the net load of nutrients from white soil is 34.1 kg ha(-1) for total nitrogen (TN), distributed as 19.4 kg ha(-1), in the rice season and 14.7 kg ha(-1) in the wheat season, and for total phosphorus (TP) 1.75 kg ha(-1), distributed as 1.16 kg ha(-1) in the rice season and 0.58 kg ha(-1) in the wheat season. The major chemical species of N loss is different in the two seasons. NH4-N is main the form in the rice season (53% of TN). NO3-N is the main form in wheat season (46% of TN). Particle-P is the main form in both seasons, (about 56% of TP). The nutrient loss varied with time of the year. The main loss of nutrients happened in the 10 days after planting, 64% of TN and 42% of TP loss, respectively. Rainfall and fertilizer application are the key factors which influence nitrogen and phosphorus loss from arable land, especially rainfall events shortly after fertilizer application. So it is very important to improve the field management of the nutrients and water during the early days of planting.     

种稻土壤CH4排放规律的研究

通过盆栽试验研究了水稻生长期CH4排放的规律。结果表明,CH4排放存在明显的日变化,最大值出现在下午4点左右,最小值出现在凌晨4点左右。土壤温度的变化是导致CH4排放日变化的主要因素。水稻生长期CH4排放的季节变化受前茬季节作物种植及稻草还田时间的显著影响。前茬季节种植紫云英及休闲且水稻移栽前施用稻草处理在水稻生长初期即有大量CH4排放,且在水稻生长的前期、中期和后期分别出现3个CH4排放峰;前茬季节种植小麦和休闲且在前茬季节前施用稻草处理的,直至水稻生长的中期才有少量CH4排放。烤田期间CH4的排放峰值出现在土壤呈微于松软状态时;烤田至土壤干裂时,CH4排放通量降至零。     

麦季稻秆还田方式对后续稻季CH4排放的影响

通过田间试验研究了麦季4种稻秆还田方式（不还田、表面覆盖、均匀混施和原位焚烧）对后续稻季CH4排放的影响,以探讨稻．麦轮作系统中秸秆还田对稻田温室气体排放的后续效应。试验于2007年小麦播种期将4．8t·hm^-2水稻秸秆分别以不同方式还田（不还田处理除外）,利用静态箱／气相色谱法对2008年后续稻季CH4排放进行观测。结果表明,不同麦季稻秆还田方式显著影响后续稻季的CH4排放。与不施稻秆处理相比,表面覆盖和均匀混施处理后续稻季CH4排放量增加了75％和40％,且CH4排放量差异主要体现在水稻生长前期（0．60d）;原位焚烧处理CH4排放量与稻秆不还田处理相比无显著差异（P〉0．05）;与不施稻秆处理相比,均匀混施处理显著增加稻季开始前土壤全C质量分数6％和全N质量分数12％（P〈0．05）;各处理水稻（Oryza sativa L．）产量无显著差异（P〉0．05）;稻秆麦季均匀混施与表面覆盖相比能在一定程度上抑制后续稻季CH4排放．同时避免了秸秆焚烧导致的C、N、P等元素的大量损失,是较为合理的麦季稻秆还田方式。     

绿黄隆、甲黄隆在江苏省农区5种土壤中残留活性的研究

采用改进的玉米主根长土培生测法，研究绿黄隆、甲黄隆在江苏省典型农区土壤中残留活性。结果表明，两种除草剂在５种土壤中剂量与玉米主根长抑制率之间皆达极显著相关，土壤ｐＨ和有机质含量是主要影响因素，碱性轻质土壤中活性较高，酸性重质土壤中活性较低，活性大小顺序为：黄潮土＞高沙土＞砂姜黑土＞滨海盐土＞太湖水稻土。     

Case Study on Nitrogen and Phosphorus Emissions from Paddy Field in Taihu Region

The agricultural non-point source pollution by nitrogen (N) and phosphorus (P) loss from typical paddy soil (whitish soil, Bai Tu in Chinese) in the Taihu Lake region was investigated through a case study. Results shown that the net load of nutrients from white soil is 34.1 kg ha^–1 for total nitrogen (TN), distributed as 19.4 kg ha^–1, in the rice season and 14.7 kg ha^–1in the wheat season, and for total phosphorus (TP) 1.75 kg ha^–1, distributed as 1.16 kg ha^–1 in the rice season and 0.58 kg ha^–1 in the wheat season. The major chemical species of N loss is different in the two seasons. NH₄-N is main the form in the rice season (53% of TN). NO₃-N is the main form in wheat season (46% of TN). Particle-P is the main form in both seasons, (about 56% of TP). The nutrient loss varied with time of the year. The main loss of nutrients happened in the 10 days after planting, 64% of TN and 42% of TP loss, respectively. Rainfall and fertilizer application are the key factors which influence nitrogen and phosphorus loss from arable land, especially rainfall events shortly after fertilizer application. So it is very important to improve the field management of the nutrients and water during the early days of planting.     

砖红壤添加铜对作物生长和残留的影响

本文对广东湛江地区砖红壤性水稻土,进行铜(CuCl_2)的不同添加浓度对水稻和花生作物生长发育和残留影响的盆栽试验研究。结果表明,在玄武岩成土母质发育的较高铜背景土壤上(46.5mg/kg),添加金属铜浓度在200mg/kg范围内,无论对水稻或花生,仍未出现对产量的不良影响,反而有一定的促进作用。从作物食用部分的残留量与土壤浓度的相关性来看,花生显著,而水稻不明显。最后建议277mg/kg土壤铜浓度作为砖红壤性水稻土的临界浓度。     

秸秆腐解剂在秸秆还田中的效果研究初报

在大田、微区和盆栽条件下,研究了秸秆腐解剂对小麦、水稻生长及产量的影响,同时研究了秸秆腐解剂对小麦、水稻秸秆腐解速率及对土壤肥力的影响。结果表明,稻、麦秸秆还田时施用秸秆腐解剂对提高稻、麦产量具有明显的增产效果,增产的原因是穗数和粒数增加;稻、麦秸秆还田量不同时,还田量大且配施秸秆腐解剂的效果较还田量小好;麦秸秆还田方式不同时,麦秸以栽稻前耕翻还田且配施秸秆腐解剂的效果较好,上水沤制的效果较差;秸秆腐解剂能促进稻、麦秸秆较快腐解,减轻和防止多量秸秆还田给作物生长带来不利影响,并可稳定和提高土壤养分含量。     

作物地上部氨排放及对大气氮沉降的吸收

为研究作物地上部分氨排放以及对大气氮沉淀的吸收情况,以水稻(Oryza saliva L.)品种武运粳7号和小麦(Triticumaestivum L.)品种扬麦15为例.在盆栽条件下,利用~15N同位素示踪技术,采用探索性的研究方法,初步分析了水稻成熟期植株NH_3排放和小麦植株直接吸收的大气沉降氮.结果表明,土培的水稻品种武运粳7号地上部植株成熟期排放氨氮(NH_3-N)量约占当季总施氮(N)量的(0.50±0.21)%;收获后水稻植株不同部位~(15)N丰度值以根部最高,茎叶次之,籽粒最低,这与植株体内养分的运移顺序变化一致;贫化~(15)N小麦砂培试验测定的包括植株直接吸收在内的大气氮沉降数量为N(14.8±4.3)kg·hm~(-2),低于国外类似方法以其它作物作为研究对象的测定结果.     

Phosphorus losses to water from lowland rice fields under rice-wheat double cropping system in the Tai Lake region

To assess P losses to surface water by runoff during the rice season and by drainage flow during the winter wheat season, serial field trials were conducted in different types of paddy soils in the Tai Lake Region (TLR) during 2000 and 2001. Four P application rates were set as 0 (CK), 30, 150, and 300 kg P/hm2 for flooded rice trials and 0 (CK), 20, 80, 160 kg P/hm2 for winter wheat trials respectively. Field experiments were done in two locations with a plot size of 30 m2 and four replications in a randomized complete block design. A simplified lysimeter was installed for each plot to collect all the runoff or drainage flow from each event. Total P (TP) losses to surface water during rice season by runoff flow from four treatments were 150 (CK), 220 (T30), 395 (T150), 670 (T300) g P/ hm2 in year 2000, and 298, 440, 1828, 3744 g P/hm2 in year 2001 respectively in Wuxi station, here the soil is permeable paddy soil derived from loam clay deposit. While the losses were 102, 140, 210, 270 in year 2000, and 128, 165, 359, 589 g P/hm2 in year 2001 respectively in Changshu station, here the soil is waterlogged paddy soil derived from silt loam deposit. During the winter wheat season, total P lost from the fields by drainage flow in the four treatments were 253 (CK), 382 (T20), 580 (T89), 818 (T160) g P/hm2 in year 2000--2001, and 573.3, 709.4, 1123.2, 1552.4 g P/hm2 in year 2001--2002 at the Wuxi station. While these were 395.6, 539.1, 1356.8, 1972.1 g P/hm2 in year 2000--2001, and 811.5, 1184.6, 3001.2, 5333.1 g P/hm2 in year 2001--2002 at the Changshu station. Results revealed that P fertilizer application rates significantly affected the TP concentrations and TP loads in runoff during the rice season, and by drainage flow during the winter wheat season. Both TP loads were significantly increased as the P application rate increases. The data indicate that TP losses to surface water were much higher during the winter wheat season than during the rice season in two tested sites. The data also reveal that the annual precipitation and evaporation rate affected the soil P losses to surface water significantly. Year 2000 was relatively dried with higher evaporation thus P losses to water by both runoff and drainage flow were less than in year 2001 which was a relatively wet year with lower evaporation. Results indicate that texture, structure of the soil profile, and field construction (with or without ridge and deep drains) affected soil P losses to surface water dramatically. Annual possible TP lost to water at the application rate of 50 kg P/hm2 year tested in TLR were estimated from 97 to 185 tones P from permeable paddy soils and 109-218 tones P from waterlogged paddy soils. There was no significant difference of TP lost between the CK and the T50 treatments in both stations, which indicate that there is no more TP lost in field of normal P fertilizer application rate than in control field of no P fertilized. Much higher TP lost in runoff or drainage flow from those other P application rates treatments than from the T50 treatment, which suggest that P losses to surface water would be greatly increasing in the time when higher available P accumulation in plough layer soil in this region.