含硅熔渣对水稻养分吸收及产量的影响

采用盆栽试验方法，研究了不同含硅熔渣对水稻养分的吸收和产量的影响，结果表明，在施用氮、磷、钾肥的基础上，增施不同类型的含硅熔渣，可提高水稻中硅和磷的含量，降低根系、茎叶和籽粒中的氮、钾含量，增加水稻对氮、磷、钾、硅的总吸收量。不同含硅熔渣的增产效果差异较大，增产最显著的是铁渣和黄磷炉渣，分别比对照增产43．4％和31．6％，施用含硅熔渣的各处理比对照平均增产19．1％，各处理间的产量经方差分析和多重比较达显著或极显著差异水平。扩散方程、Elovich方程和多项式方程均能很好地描述水稻生长期内水稻对N、P、K、Si的吸收过程，尤以多项式方程拟合最佳。     

糯稻和非糯稻蜡质基因的新STS分子标记

通过对前人公布的糯性水稻蜡质基因全序列测定结果的分析,根据糯性水稻与非糯性水稻蜡质基因序列位点的差异,设计了两个基于PCR扩增反应的可特异识别糯性水稻的显性和共显性STS分子标记;同时在前人公布的非糯性水稻蜡质基因的不同类型(Wxa和Wxb)的全序列比对分析的基础上,选取了两种基因型特定的差异位点,设计了两个基于PCR扩增反应用于特异识别这两种Wx基因的显性STS分子标记,并用新建立的标记对相应的水稻基因型进行了检测.图2表2参10     

杂草对不同水稻品种化感作用的诱导效应

以高脚子粳稻、DV86、HG1和扬稻6号4个水稻品种和稗草、异型莎草、鸭舌草为材料，研究了不同水稻品种单栽或与杂草共栽时，水稻叶片水浸提液对稻田主要杂草稗草的化感作用。结果表明：在正常单栽条件下，高脚子粳稻抗稗草的化感潜力显著大于：HG1和DV86，三者的化感潜力均显著大于非化感品种扬稻6号。不同水稻品种与杂草共栽时，其化感作用均由不同程度的变化，HG1在与稗草共栽时，对稗草幼苗的生长抑制作用显著大于高脚子粳稻；DV86在与鸭舌草共栽时，对稗草幼苗的生长抑制最强。研究表明不同杂草对不同水稻品种的杂草化感作用的诱导效应存在显著差异。     

磷胁迫对水稻基因型根系形态及吸收铁锰铜锌的影响

采用营养液培养方法研究了缺磷胁迫下4种水稻基因型(90-90—1、金23A、90-68-1、CDR22)的根系形态变化情况及其吸收微量元素铁、锰、铜、锌的影响。结果表明，(1)磷胁迫下，每个基因型在磷胁迫下其根系形态发生了明显变化、如根长、根冠比均呈增加趋势，并且根表有红棕色铁氧化物膜包被。(2)磷胁迫下根系形态的变化影响了水稻对生长介质中铁、锰、铜、锌的吸收：正常水稻植株中铁、锰、锌的含量高于磷胁迫植株，其中磷营养状况对水稻吸收铁、锰影响最明显；而磷营养状况对水稻植株铜含量的影响与铁、锰、锌正好相反，且影响程度较小。     

铅在紫色土—水稻体系中的植物效应及形态

本文研究了酸性、中性及石灰性紫色土中铅的水稻效应、形态特征及有效性。酸性与石灰性紫色土中水稻分别在含铅量1000、2000mg/kg时出现明显受害,中性紫色土在4000mg/kg时亦无明显影响。水稻各部位含铅量是酸性>石灰性>中性紫色土,并与添加铅呈显著正相关,且其大小顺序为根>茎叶>糙米。铅90％以上积累于水稻根部;施铅使土壤中无效铅比例下降。有效性较高的铅形态比例上升。交换态、碳酸盐态或弱结合态铅含量较高的土壤上,水稻反应大。用有效态铅为指标有可能使不同土壤铅临界浓度比较接近一致。     

重金属在土壤-水稻体系中的分布、变化及迁移规律分析

以佛山市南海区小塘镇和高明区杨梅镇的标准农田为研究对象,分析重金属在土壤和水稻植株不同部位的分布及其随时间变化、迁移规律。结果表明:重金属被水稻吸收以后,多数仍滞留在土壤里,只有少量向地上部分迁移。重金属在水稻植株不同部位的质量分数分布由大到小的次序为:根→茎→籽→叶。水稻地上部分中4种重金属元素分布由大到小的次序是:Zn→Cu→Pb→Cd。水稻分蘖期重金属在根、茎和叶的积累量达到最大,随着时间的延续,在根部积累的重金属就越来越少,茎和叶积累的重金属在拔节期降至最小,随后又慢慢上升。4种重金属在水稻植株中的迁移能力由大到小依次为:Cd→Zn→Cu→Pb,但也有个别情况是Cu的迁移能力大于Zn。     

Elevated Levels of Cadmium and Zinc in Paddy Soils and Elevated Levels of Cadmium in Rice Grain Downstream of a Zinc Mineralized Area in Thailand: Implications for Public Health

Prolonged consumption of rice containing elevated cadmium (Cd) levels is a significant health issue particularly in subsistence communities that are dependent on rice produced on-farm. This situation is further exacerbated in areas of known non-ferrous mineralization adjacent to rice-based agricultural systems where the opportunity for contamination of rice and its eventual entry into the food chain is high. In the current study, an assessment of the degree of soil Cd and Zn contamination and associated rice grain Cd contamination downstream of an actively mined zone of Zn mineralization in western Thailand was undertaken. Total soil Cd and Zn concentrations in the rice-based agricultural system investigated ranged from 0.5 to 284 mg kg⁻¹ and 100 to 8036 mg kg⁻¹, respectively. Further, the results indicate that the contamination is associated with suspended sediment transported to fields via the irrigation supply. Consequently, the spatial distribution of Cd and Zn is directly related to a field’s proximity to primary outlets from in-field irrigation channels and inter-field irrigation flows with 60–100% of the Cd and Zn loading associated with the first three fields in irrigation sequence. Rice grain Cd concentrations in the 524 fields sampled, ranged from 0.05 to 7.7 mg kg⁻¹. Over 90% of the rice grain samples collected contained Cd at concentrations exceeding the Codex Committee on Food Additives and Contaminants (CCFAC) draft Maximum Permissible Level for rice grain of 0.2 mg Cd kg⁻¹. In addition, as a function of demographic group, estimated Weekly Intake (WI) values ranged from 20 to 82 μg Cd per kg Body. This poses a significant public health risk to local communities. The results of this study suggest that an irrigation sequence-based field classification technique in combination with strategic soil and rice grain sampling and the estimation of WI values via rice intake alone may be a useful decision support tool to rapidly evaluate potential public health risks in irrigated rice-based agricultural systems receiving Cd contaminated irrigation water. In addition, the proposed technique will facilitate the cost effective strategic targeting of detailed epidemiological studies thus focusing resources to specific ‘high risk’ areas.     

水稻耐低磷特性研究

选取3个耐低磷水稻基因型99011、580、99112和1个磷敏感基因型99056为供试材料，采用营养液和石英砂培养的方法，研究了与磷效率相关的一些指标．结果表明，99011和580均具有较高的磷吸收效率和利用效率，其中根长是99011高效吸收的重要贡献因子，其次它对难溶性磷有一定的活化吸收能力；580不仅对难溶性磷的活化吸收能力最强，而且善于从低浓度的磷环境中吸收较多的磷；而99112主要靠被动适应生态环境来表现它的耐低磷特性，与磷吸收效率相关的次级因子表现不佳，是99056对低磷反应敏感的主要原因．图3表4参16     

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。     

Effect of application of ammonium thiosulphate on production and emission of methane in a tropical rice soil

Agricultural sources of atmospheric methane include flooded rice (Oryza sativa L.) paddies. However, certain soil nutrient management and cultural practices offer opportunities to reduce methane emissions. The effect of application of ammonium thiosulphate, a potential source of nitrogen and sulphur and also an inhibitor of nitrification and urease on methane production and emission from flooded alluvial (Typic Haplaquept) rice soil in India, was examined. Methane production and emission from control and urea-amended soil samples were almost identical. Application of ammonium thiosulphate to laboratory-incubated flooded soil (30 and 60 μg N g⁻¹ soil) and flooded rice fields (45.6 and 60 kg N ha⁻¹) effected a distinct inhibition of methane production and emission. Ammonium thiosulphate stimulated the population of sulphate-reducing bacteria (SRB) to a greater extent at 60 μg N g⁻¹ soil than at 30 μg N g⁻¹ soil. In ammonium thiosulphate-applied rice field plots, mean methane efflux decreased by about 38 and 60% at 45.6 and 60 kg N ha⁻¹, respectively, over that of control. Inhibition of methane production by ammonium thiosulphate is, at least in part, due to the stimulation of SRB. Results suggest the mitigation potential of ammonium thiosulphate on methane emission from flooded rice paddies.