WO2015096533A1 - 一种可以抑制水稻重金属吸收积累生产富硒稻米的硒掺杂纳米硅溶胶及其制备方法 - Google Patents

一种可以抑制水稻重金属吸收积累生产富硒稻米的硒掺杂纳米硅溶胶及其制备方法 Download PDF

Info

Publication number
WO2015096533A1
WO2015096533A1 PCT/CN2014/088288 CN2014088288W WO2015096533A1 WO 2015096533 A1 WO2015096533 A1 WO 2015096533A1 CN 2014088288 W CN2014088288 W CN 2014088288W WO 2015096533 A1 WO2015096533 A1 WO 2015096533A1
Authority
WO
WIPO (PCT)
Prior art keywords
selenium
silica sol
doped
solution
rice
Prior art date
Application number
PCT/CN2014/088288
Other languages
English (en)
French (fr)
Inventor
刘传平
李芳柏
崔江虎
徐向华
Original Assignee
广东省生态环境与土壤研究所（广东省土壤科学博物馆）
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by 广东省生态环境与土壤研究所（广东省土壤科学博物馆） filed Critical 广东省生态环境与土壤研究所（广东省土壤科学博物馆）
Priority to JP2015554051A priority Critical patent/JP6068679B2/ja
Priority to US14/771,189 priority patent/US9919978B2/en
Publication of WO2015096533A1 publication Critical patent/WO2015096533A1/zh

Links

Images

Classifications

    • C—CHEMISTRY; METALLURGY
    • C05—FERTILISERS; MANUFACTURE THEREOF
    • C05D—INORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C; FERTILISERS PRODUCING CARBON DIOXIDE
    • C05D9/00—Other inorganic fertilisers
    • C05D9/02—Other inorganic fertilisers containing trace elements
    • A—HUMAN NECESSITIES
    • A01—AGRICULTURE; FORESTRY; ANIMAL HUSBANDRY; HUNTING; TRAPPING; FISHING
    • A01N—PRESERVATION OF BODIES OF HUMANS OR ANIMALS OR PLANTS OR PARTS THEREOF; BIOCIDES, e.g. AS DISINFECTANTS, AS PESTICIDES OR AS HERBICIDES; PEST REPELLANTS OR ATTRACTANTS; PLANT GROWTH REGULATORS
    • A01N59/00—Biocides, pest repellants or attractants, or plant growth regulators containing elements or inorganic compounds
    • A01N59/02—Sulfur; Selenium; Tellurium; Compounds thereof

Definitions

  • the invention belongs to the field of soil and fertilizer, and particularly relates to a selenium-doped nano-silica sol which can inhibit the absorption and accumulation of heavy metals in rice to produce selenium-enriched rice and a preparation method thereof.
  • Selenium is an essential trace element in animals and human body. It is a component of glutathione peroxidase and has an antioxidant effect. In 1973, the World Health Organization (WHO) announced that selenium is an essential nutrient for the human body; in 1988, the Chinese Nutrition Society listed selenium as a necessary nutrient for humans. Selenium has many physiological functions in humans and animals: selenium has anti-cancer, anti-tumor and anti-aging effects.
  • Endemic diseases in China such as Keshan disease and Kashin-Beck disease, are closely related to selenium deficiency in the environment. Therefore, selenium plays an important role in human health.
  • the selenium required by the human body must be obtained from the diet.
  • the International Selenium Society recommends that the daily intake of selenium in humans is 60-400 ⁇ g, and the recommended daily intake of the Chinese Nutrition Society is 50-200 ⁇ g.
  • the China Nutrition Society survey shows that the average daily selenium intake of Chinese residents is only 26-32 ⁇ g; the number of selenium-deficient provinces in China is as high as 22, and the selenium-deficient area accounts for about 72% of the country's land area.
  • selenium-enriched fertilizers By increasing the resistance of rice to selenium nutrition to heavy metals, it can not only reduce the absorption and accumulation of heavy metals in rice, but also increase the level of selenium enrichment in rice. Therefore, the development and application of selenium-enriched fertilizers have received extensive attention.
  • the selenium-enriched fertilizers at home and abroad mainly include water-soluble foliar selenium-enriched fertilizer, inorganic organic selenium-rich compound fertilizer, and selenium-enriched slow-release fertilizer.
  • selenium-enriched fertilizers Although there are many patents for the preparation of selenium-enriched fertilizers, most of them are simply prepared by simply mixing inorganic selenite with livestock manure or agricultural waste or by microbial fermentation.
  • Fertilizers prepared by these methods have a low selenium content and often contain less than 0.1% selenium, and the inorganic selenite itself is biologically toxic. The applied dose is too large to cause damage to the crop, and the application safety is poor.
  • the preparation of high-activity, safe and efficient selenium-enriched foliar silicon fertilizer with nano-silica sol as a carrier has not been reported. Silicon is a special beneficial element. Regulating the silicon nutrition of rice can increase the heavy metal resistance of crops and inhibit the absorption of crops. metal.
  • selenium-doped foliar silicon fertilizer will inevitably improve the absorption performance of heavy metal in crops, and at the same time produce selenium-enriched agricultural products; it not only meets the demand for selenium-enriched agricultural products, but also provides for the treatment of heavy metals in farmland soils in China. A new way out.
  • the object of the present invention is to provide a safe and efficient selenium-doped nano-silica sol which can inhibit the absorption and accumulation of heavy metals in rice and can produce selenium-enriched rice, can inhibit the absorption and accumulation of heavy metals in rice, and produce a selenium-enriched rice, and a preparation method thereof.
  • the preparation method has the advantages of simple process and low production cost, and the prepared selenium-doped nano-silica sol product capable of inhibiting the absorption and accumulation of heavy metals in rice to produce selenium-enriched rice has stable performance, a particle size of less than 50 nm and uniform distribution, and the product is a uniform transparent sol, pH. Close to neutral, it can be widely used to inhibit the absorption and accumulation of heavy metals by crops, and at the same time produce selenium-enriched rice.
  • the selenium-doped nano-silica sol which can inhibit the absorption and accumulation of heavy metals in rice and produce selenium-enriched rice mainly uses nano silica sol as a carrier, sodium selenite as a raw material, vitamin C as a reducing agent, polyvinylpyrrolidone, etc.
  • An emulsifier that selenium is doped in a specific ratio and dispersed into a silica sol to form a selenium-doped nanosilica sol having a special structure and function capable of inhibiting absorption and accumulation of heavy metals in rice to produce selenium-enriched rice.
  • the selenium-doped nano-silica sol of the invention capable of inhibiting the absorption of heavy metals in rice to produce selenium-enriched rice is prepared by the following method, and the preparation method comprises the following steps:
  • metal silicate solution metal silicon powder or metal silicate is added to an alkaline solution having a concentration of 0.1 to 5 M under stirring to prepare a metal silicate solution containing metal silicon powder or The concentration of the metal silicate is 5% by weight to saturation, and the pH is 10-13; the metal silicate is Na 2 SiO 3 , K 2 SiO 3 or Li 2 SiO 3 ;
  • emulsified selenium doping solution under stirring, the emulsifier is added to the acidic selenium doping solution of step (3), and the mass percentage of the final emulsifier is controlled at 0.05 to 5%, thereby obtaining emulsified selenium doping.
  • the emulsifier is polyvinylpyrrolidone (PVP), polyvinyl alcohol (PVA), Tween series or Span series;
  • preparing a selenium-doped acidic silica sol precursor the emulsified selenium doping solution of the step (4) is added to the acidic silica sol precursor of the step (2) under stirring to obtain a selenium-doped acidic silica sol precursor.
  • the mass percentage of silicon:selen in the selenium-doped acidic silica sol precursor is 3 to 200:1;
  • the alkaline solution of the step (1) is prepared by using sodium hydroxide, potassium hydroxide or ammonia water, preferably at a concentration of 0.1 to 2M.
  • the pH of the collected liquid in the step (2) is preferably 2 to 3.5, and the heating temperature of the collecting liquid is preferably 45 to 55 °C.
  • the dilute acid solution of the step (3) may be hydrochloric acid, nitric acid, sulfuric acid, phosphoric acid or the like, preferably hydrochloric acid; the acid selenium doping liquid preferably has a selenium content mass percentage of 2 to 7.6%; The pH of the liquid is preferably controlled to be 1-2.
  • the emulsifier described in the step (4) is preferably tempered, and the final emulsifier mass percentage is preferably controlled to 0.5 to 2%.
  • the mass percentage of silicon:selenium in the selenium-doped acidic silica sol precursor of the step (5) is preferably from 9 to 20:1.
  • the temperature of the alkaline solution prepared by the alkaline catalyst of the step (6) is preferably controlled at 45 ° C to 85 ° C, and the stirring reaction is continued for 30 to 60 min.
  • the reducing agent of the step (7) is preferably ascorbic acid (Vc), and the temperature of the solution is preferably controlled to be 50 ° C to 85 ° C.
  • the selenium-doped nano-silica sol prepared by the invention can inhibit the absorption and accumulation of heavy metals in rice to produce selenium-enriched rice, has high stability, high concentration and uniform transparency, and has the following advantages compared with the prior art:
  • the selenium-doped nano-silica sol prepared by the method of the invention has a silica content of more than 20%, a selenium content of more than 1%, and a low impurity content.
  • the pH of the selenium-doped nano-silica sol of the present invention is close to neutral, and the selenium is dispersed in the middle of the silica colloid with the nano-particles, and the colloidal particle size is less than 50 nm. After spraying on the foliar surface, the growth of the crop can be significantly promoted and inhibited. The absorption of arsenic by crops accumulates, and the selenium content of crops is increased, and there is no toxic side effect on crops, and the application is safe.
  • the preparation method of the present invention is carried out at a lower temperature and a normal pressure, the conditions are mild, the process is simple, and the operation is easy, so that mass production is easy. And its raw materials are widely sourced, the cost is lower and the output is larger, which is conducive to promotion.
  • Example 1 is a scanning electron micrograph of a 1% selenium doped silica sol of Example 1;
  • Example 2 is a particle size distribution of a 1% selenium doped silica sol of Example 1;
  • Figure 3 is a diagram showing the effect of spraying different fertilizers on the dry weight of rice grains in the pot experiment of Example 4.
  • Figure 4 is a diagram showing the effect of spraying different fertilizers on the arsenic content of rice in the pot experiment of Example 4;
  • Figure 5 is a diagram showing the effect of spraying different fertilizers on the selenium content of rice in the pot experiment of Example 4;
  • 6 is a graph showing the effect of spraying different concentrations of selenium-doped silica sol on the arsenic content of arsenic-contaminated rice in Yanhong Town;
  • Figure 8 is a graph showing the effect of spraying different concentrations of selenium-doped silica sol on the cadmium content of cadmium-contaminated farmland in Handan City;
  • Figure 9 is a graph showing the effect of spraying different concentrations of selenium-doped silica sol on the selenium content of rice in cadmium-contaminated farmland in Handan City.
  • Example 1 Preparation of selenium-doped nanosilica sol which can inhibit the absorption and accumulation of heavy metals in rice and produce selenium-enriched rice
  • the selenium-doped acidic silica sol precursor is slowly added to 20 ml of 25-28% ammonia water, stirred while stirring, and kept at a temperature of 45 ° C. After the addition is completed, the pH is 7-7. Between 9 and further, the reaction was stirred at 45 ° C for 30 min to obtain a selenium-doped silica sol precursor.
  • the selenium-doped silica sol precursor liquid is slowly added to 50 mL of 0.1 M ascorbic acid (Vc) heated to 50 ° C by microwave (or water bath), and added dropwise, until the sol red color is no longer deepened, and the selenium is sufficiently reduced. Stirring was continued for more than 2 hours to obtain a sol.
  • the prepared sol was subjected to two dialysis and concentrated to 200 mL by evaporation to obtain a uniformly stable and translucent high-purity selenium-doped nanosilica sol, which was inhibited in this example.
  • Heavy metal absorption in rice accumulates and produces selenium-doped nano-silica sols for selenium-enriched rice.
  • the prepared high-purity selenium-doped nano-silica sol has a silica content of 20% and a selenium content of 0.1%, 0.5%, 1% and 2%, respectively.
  • Figure 1 is a scanning electron micrograph of a selenium-doped nanosilica sol having a selenium content of 1%
  • Fig. 2 is a particle size distribution of a selenium-doped nanosilica sol having a selenium content of 1%.
  • Example 2 Preparation of selenium-doped nanosilica sol which can inhibit the absorption and accumulation of heavy metals in rice and produce selenium-enriched rice
  • the above metal silicate solution is passed through a 100 mL (wet volume) hydrogen type strong acid cation multi-stage resin exchange column at a rate of 5 mL/min, and the pH of the outlet of the control column is between 2.5 and 3.5, and the collected liquid is microwaved. (or water bath) stirring and heating to 90 ° C, static cooling and aging for 30 min, the acidic silica sol precursor is obtained, ready for use.
  • the above emulsified selenium doping solution is added dropwise to the above-mentioned selenium-doped acidic silica sol precursor, and stirred while maintaining the temperature at 85 ° C; after the addition, stirring is continued for 90 min to obtain Selenium doped acidic silica sol precursor. Then, the selenium-doped acidic silica sol precursor is slowly added to 20 ml of sodium hydroxide having a concentration of 0.5-1.2 M, and stirred while maintaining the temperature at 85 ° C. After the completion of the dropwise addition, the pH is at Between 7 and 9, the reaction was further stirred at 85 ° C for 30 min to obtain a selenium-doped silica sol precursor.
  • the selenium-doped silica sol precursor solution is slowly added to 50 mL of 0.5 M glutathione heated to 85 ° C by microwave (or water bath), and added dropwise until the sol red color is no longer deepened, and the selenium is sufficiently reduced. Stirring was continued for more than 2 hours to obtain a sol.
  • the prepared sol was subjected to two dialysis and concentrated to 200 mL by evaporation to obtain a uniformly stable and translucent high-purity selenium-doped nanosilica sol, which was inhibited in this example. Heavy metal absorption in rice accumulates and produces selenium-doped nano-silica sols for selenium-enriched rice.
  • the prepared high-purity selenium-doped nano-silica sol has a silica content of 15% and a selenium content of 0.12%, 0.58%, 1.5% and 2.3%, respectively.
  • Example 3 Preparation of selenium-doped nanosilica sol which can inhibit the absorption and accumulation of heavy metals in rice and produce selenium-enriched rice
  • the salt has a mass fraction of 20%.
  • the above metal silicate solution is passed through a 100 mL (wet volume) hydrogen type strong acid cation multi-stage resin exchange column at a rate of 5 mL/min, and the pH of the outlet of the control column is between 2.5 and 3.5, and the collected liquid is microwaved. (or water bath) stirring and heating to 35 ° C, static cooling and aging for 30 min, the acidic silica sol precursor is obtained, ready for use.
  • the emulsified selenium doping solution is added dropwise to the selenium-doped acidic silica sol precursor, and stirred while maintaining the temperature at 35 ° C; after the addition, stirring is continued for 30 min to obtain a selenium-doped acidic silica sol precursor. . Then, the selenium-doped acidic silica sol precursor is slowly added to 20 ml of potassium hydroxide having a concentration of 0.1-0.5 M, and stirred while maintaining the temperature at 35 ° C. After the dropwise addition, the pH is at Between 7 and 9, the reaction was further stirred at 35 ° C for 60 min to obtain a selenium-doped silica sol precursor.
  • the selenium-doped silica sol precursor liquid is slowly added to 50 mL of 0.1 M glucose heated to 35 ° C by microwave (or water bath), dropwise, until the sol is reddish, the selenium is fully reduced, and stirring is continued. After 2 hours or more, the sol is obtained, and the prepared sol is subjected to two dialysis and concentrated to 200 mL by evaporation to obtain a uniformly stable and translucent high-purity selenium-doped nano-silica sol, which can inhibit the absorption of heavy metals in rice. Accumulate selenium-doped nano-silica sol for producing selenium-enriched rice.
  • the prepared high-purity selenium-doped nano-silica sol has a silica content of 10% and a selenium content of 0.1%, 0.2%, 0.4%, and 0.8%, respectively.
  • Example 4 Effect of foliar application of selenium-doped nano-silica sol on mitigation of heavy metals in rice
  • the tested soil was collected from an arsenic-contaminated paddy field in Yanhong Town, Chenghai District, Shantou City, Guangdong province.
  • the soil was taken from the surface of the paddy field (0-10 cm). After air drying, it was sieved, and 10 kg of soil was placed in the barrel.
  • the soil was basically physical and chemical. The properties are as follows: pH 6.12, organic matter 2.73%, total nitrogen 1.5g/kg, total phosphorus 1.02g/kg, total potassium 11.3g/kg, CEC 8.75cmol/kg, total arsenic 93.6mg/kg, total selenium 0.879mg/ Kg.
  • Rice cultivation and treatment The rice variety is Youyou 128.
  • the surface of rice seeds was sterilized with 5% sodium hypochlorite solution for 15 minutes. After rinsing with tap water, germination and seedlings were planted, and uniform seedlings were selected for transplanting.
  • foliar application of silica sol or the 1% selenium-doped nanosilica sol of Example 1 can significantly promote rice growth, and the dry weight of rice grains increased by 20.2% compared with the control. 43.8%; compared with foliar application of silica sol, foliar application of 1% selenium-doped nano-silica sol promoted the growth of rice more significantly.
  • the aqueous solution prepared by spraying 1% sodium selenite on the foliar surface had an inhibitory effect on rice growth; the dry weight of rice grain decreased by 13.1% compared with the control.
  • Foliar application of selenium-doped nano-silica sol can not only promote rice growth, but also inhibit the accumulation of arsenic in rice and increase the selenium content of rice.
  • the arsenic content of rice decreased by 46% after spraying 1% selenium-doped nano-silica sol, while the arsenic content of rice decreased by 28% after spraying pure silica sol, and 1% sodium selenite was sprayed. After the aqueous solution, the arsenic content of rice decreased by 19%.
  • the selenium content of rice increased from 0.050 mg/kg to 0.272 mg/kg; the selenium-enriched rice standard was reached.
  • the selenium content of the rice prepared by spraying 1% sodium selenite on the foliar surface was 0.180 mg/kg; only 66% of the 1% selenium-doped nano-silica sol rice was sprayed on the foliar surface.
  • Example 5 Foliar application of selenium-doped nano-silica sol to reduce the effect of heavy metal arsenic absorption in rice field
  • Spraying time During the rice tillering period (about 60 days), spray at about 4 o'clock in the afternoon when sunny or cloudy weather is selected; if it rains within 24 hours after spraying, it will be sprayed once.
  • the series concentration gradient of selenium-doped nano-silica sol produced in Example 1 has a silicon content of 20% and a selenium content of 0.1%, 0.5%, 1% and 2%, about 1L per acre, foliar spray with 100L of water; spray the same amount of clean water as control; respectively recorded as 0.1% Se-Si, 0.5% Se-Si, 1% Se-Si, 2 %Se-Si, CK.
  • Each of the 4 cells is processed, and the random blocks are arranged.
  • the selenium doping concentration reaches 0.5%
  • the arsenic content of rice meets the national food safety standards (inorganic arsenic ⁇ 0.2mg/kg GB2762-2012); and when the selenium doping amount is 0.1% and 0.5%, the selenium in rice The contents are 0.12 mg/kg and 0.26 mg/kg, respectively, in line with the selenium-enriched rice standard. Therefore, in Yanhong Town, 90% selenium-doped nano-silica sol can be sprayed on the arsenic-contaminated farmland to produce selenium-enriched rice with arsenic content up to standard.
  • Example 6 Foliar application of selenium-doped nano-silica sol to reduce the absorption of heavy metals, cadmium and arsenic in rice
  • the selenium doping concentration reaches 1%
  • the cadmium content of rice drops below 0.2mg/kg, which meets the national food safety standards (cadmium ⁇ 0.2mg/kg GB 2762-2012); and when the selenium doping amount is 0.5% and At 1%, the selenium content in rice was 0.16 mg/kg and 0.28 mg/kg, respectively; meeting the selenium-enriched rice standard. Therefore, in the town of Handan City, the selenium-enriched rice with cadmium content can be produced on the cadmium-contaminated farmland by spraying the 1% selenium-doped nano-silica sol on the leaf surface.

Landscapes

  • Life Sciences & Earth Sciences (AREA)
  • Chemical & Material Sciences (AREA)
  • Inorganic Chemistry (AREA)
  • Health & Medical Sciences (AREA)
  • General Health & Medical Sciences (AREA)
  • Dentistry (AREA)
  • Environmental Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Pest Control & Pesticides (AREA)
  • Agronomy & Crop Science (AREA)
  • Wood Science & Technology (AREA)
  • Zoology (AREA)
  • Plant Pathology (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Organic Chemistry (AREA)
  • Fertilizers (AREA)
  • Toxicology (AREA)
  • Cultivation Of Plants (AREA)
  • Agricultural Chemicals And Associated Chemicals (AREA)

Abstract

一种可以抑制重金属吸收积累生产富硒稻米的硒掺杂纳米硅溶胶及其制备方法。硒掺杂纳米硅胶其主要以纳米硅溶胶为载体，以亚硒酸钠等为原料，维生素C等作为还原剂，聚乙烯吡咯烷酮等为乳化剂，将硒以特定比例掺杂、并分散到硅溶胶中形成具有特殊结构和功能的硒掺杂纳米硅溶胶。制备得到的硒掺杂纳米硅溶胶稳定性高，浓度高，均一透亮，其二氧化硅含量可达20%以上，硒含量可达1%以上，且杂质含量少。硒掺杂纳米硅溶胶的pH接近中性，硒以纳米颗粒分散于二氧化硅胶体中间，胶体粒径小于50纳米，在叶面喷施后，可以显著促进作物生长，抑制作物对砷、镉的吸收积累，且增加作物硒含量，且对农作物无毒副作用，施用安全。

Description

一种可以抑制水稻重金属吸收积累生产富硒稻米的硒掺杂纳米硅溶胶及其制备方法 技术领域：
本发明属于土壤肥料领域，具体涉及一种可以抑制水稻重金属吸收积累生产富硒稻米的硒掺杂纳米硅溶胶及其制备方法。
背景技术：
硒是动物和人体的必需微量元素，是谷胱甘肽过氧化物酶的组成成分，具有抗氧化作用。1973年世界卫生组织(WHO)宣布：硒是人体必须营养元素；1988年中国营养学会把硒列为人类必须营养元素。硒在人和动物体中具有多种生理功能：硒具有防癌、抗肿瘤和抗衰老的等作用。我国的地方病，如克山病、大骨节病等都与环境中缺硒密切相关。因此，硒对人体健康有着重要的作用。
人体所需要的硒必须从饮食中获取，国际硒学会推荐人体硒日摄入量为60-400μg，我国营养学会推荐日摄入量为50-200μg。但是中国营养学会调查表明，我国居民平均日硒摄入量仅为26-32μg；我国缺硒的省份多达22个，缺硒面积约占国土面积的72％。虽然可以通过食品添加剂、保健品或药物来快速补充人体缺乏的硒，但是这一补硒方式费用高、覆盖面小，不能从根本上解决大面积缺硒地区人体硒营养的有效补充。提高农产品硒含量是从源头预防人体硒缺乏疾病的根本出路。其中水稻是我国的主要粮食作物，因此提高稻米中硒含量，生产富硒大米对人体硒营养以及健康有着重要的意义。
同时有文献报道硒可以降低水稻对重金属砷、铅、镉、铬等元素的吸收积累；提高水稻抗重金属能力。土壤重金属污染问题是土壤最主要也是最严重的污染问题之一，受到了全球广泛关注和重视。我国土壤重金属污染问题也十分突出，大约六分之一的基本耕地受到不同 程度的重金属污染；我国仅受Cd污染的农田就到1.2万公顷。据估算全国每年因重金属污染的粮食达1200万吨，造成的直接经济损失超过200亿元。由土壤污染引发的农产品质量安全问题和群体性事件逐年增多，成为影响群众身体健康和社会稳定的重要因素。目前国内外土壤重金属污染修复方法主要包括物理修复、化学修复和生物修复方法等。物理、化学修复方法适用于污染范围小、污染严重的集中场地，往往工程量大、成本高，且常常导致土壤结构破坏和某些营养元素的淋失。生物修复方法特别是植物修复技术是目前较推崇的方法，因其环境友好、成本低、不产生二次污染等优点成为当前国内外的研究热点和前沿领域。但是由于植物修复技术对高污染浓度或复合污染的不适应性、修复植物不适宜污染当地的土壤特性和气候等，并不完全能适应农田重金属污染治理，而且现阶段尚未能达到实际应用水平，植物修复技术目前仍难未能得到商业化的应用。而从农作物营养生理调控的角度，提高农作物的重金属抗性，抑制农作物吸收积累重金属，为解决区域性的农田生态安全问题提供新的思路。
通过增加水稻硒营养提水稻对重金属的抗性，不仅可以降低水稻对重金属的吸收积累，同时可以提高稻米硒富集水平。因此，富硒肥料的研发和施用受到了广泛的关注。国内外富硒肥料主要有水溶性叶面富硒肥料、无机有机富硒复混肥料、富硒缓释肥料等。虽然目前富硒肥料制备专利很多，但是大多数是简单将无机亚硒酸盐与畜禽粪便或农业废弃物进行简单混合或经微生物发酵后制备而成。利用这些方法制备的肥料，含硒量较低往往含硒量不足0.1％，且无机亚硒酸盐本身是具有生物毒性的，施用剂量过大会对作物造成伤害，施用安全性较差。而以纳米硅溶胶为载体，制备活性高、安全高效的富硒叶面硅肥的工艺还未见报道。硅是特殊的有益元素，调控水稻的硅营养均可提高农作物的重金属抗性，抑制农作物吸收重 金属。我们前期的专利技术：“一种可抑制水稻吸收重金属的稀土复合硅溶胶(ZL200610036994.8)”、“一种用于降低蔬菜重金属和硝酸盐含量的复合叶面硅肥及其制备方法(ZL 201010156359.X)”和“一种叶面硅肥的制备方法及使用方法(ZL201010156358.5)”开发的是叶面硅肥、或者是微量元素掺杂叶面硅肥、或者是稀土元素掺杂叶面硅肥。目前国内还没有硒掺杂叶面硅肥产品。由于硒具有特殊的生理功能，又可以提高农作物对重金属的抗性。因此，制备硒掺杂叶面硅肥，必然将提高硅肥产品抑制农作物重金属吸收性能，同时又可以生成出富硒农产品；既满足了富硒农产品的生成需求，又为我国农田土壤重金属治理提供新的出路。
发明内容：
本发明的目的是提供一种安全高效的、既可以抑制水稻重金属吸收积累，又可以生产富硒稻米的可以抑制水稻重金属吸收积累生产富硒稻米的硒掺杂纳米硅溶胶及其制备方法，该制备方法工艺简单，生产成本低廉，所制备得到的可以抑制水稻重金属吸收积累生产富硒稻米的硒掺杂纳米硅溶胶产品性能稳定、粒径小于50纳米且分布均匀，产品为均一透明溶胶，pH接近中性，可以广泛应用于抑制农作物对重金属吸收积累、且同时生产富硒大米等方面。
本发明的可以抑制水稻重金属吸收积累生产富硒稻米的硒掺杂纳米硅溶胶其主要以纳米硅溶胶为载体，以亚硒酸钠等为原料，维生素C等作为还原剂，聚乙烯吡咯烷酮等为乳化剂，将硒以特定比例掺杂、并分散到硅溶胶中形成具有特殊结构和功能的可以抑制水稻重金属吸收积累生产富硒稻米的硒掺杂纳米硅溶胶。
本发明的可以抑制水稻重金属吸收积累生产富硒稻米的硒掺杂纳米硅溶胶，其是通过以下方法制备的，该制备方法包括以下步骤：
(1)配制金属硅酸盐溶液：将金属硅粉或金属硅酸盐在搅拌条件加入到浓度为0.1～5M的碱性溶液中，配制成金属硅酸盐溶液，其中含的金属硅粉或金属硅酸盐的浓度为重量百分比5％至饱和，pH为10～13；所述的金属硅酸盐为Na2SiO3、K2SiO3或Li2SiO3；
(2)制备酸性硅溶胶前驱物：将金属硅酸盐溶液经过阳离子交换处理，控制收集液pH为1～4，将收集液加热到35-90℃，再静止冷却陈化，得到酸性硅溶胶前驱物；
(3)制备酸性硒掺杂液：将含硒化合物在搅拌条件下溶解到稀酸溶液中，制备硒含量质量百分比为0.1-10％的酸性硒掺杂液，酸性硒掺杂液的pH值控制为1～4；所述的含硒化合物为亚硒酸、亚硒酸钠、亚硒酸钾或者亚硒酸氢钠；
(4)制备乳化硒掺杂液：在搅拌条件下，将乳化剂加入到步骤(3)的酸性硒掺杂液中，最终乳化剂质量百分数控制在0.05～5％，由此得到乳化硒掺杂液；所述的乳化剂为聚乙烯吡咯烷酮(PVP)、聚乙烯醇(PVA)、吐温系列(Tween)或斯潘系列；
(5)制备硒掺杂酸性硅溶胶前驱物：将步骤(4)的乳化硒掺杂液在搅拌条件下加入到步骤(2)的酸性硅溶胶前驱物中，得到硒掺杂酸性硅溶胶前驱物，其中硒掺杂酸性硅溶胶前驱物中的硅：硒的质量百分比为3～200：1；
(6)将步骤(5)的硒掺杂酸性硅溶胶前驱物加入到30℃～90℃的碱性催化剂配制的碱溶液中，直至碱溶液的pH值到7～9之时停止加入，继续搅拌反应30～90min，得到硒掺杂硅溶胶前体；所述的碱性催化剂为氢氧化钠、氢氧化钾、尿素、氨水或者硅酸钠溶液；
(7)将步骤(6)的硒掺杂硅溶胶前体加入到30℃～90℃的还原剂溶液中，直至溶胶淡红色不再加深，硒充分还原后，继续搅拌反应2小时以上，然后再经2次以上渗析，即得到可以抑制水稻重金属吸收积累生产富硒稻米的硒掺杂纳米硅溶胶；所述的还原剂为抗坏血酸 (Vc)、谷胱甘肽或还原性糖类。
所述的步骤(1)的碱性溶液是用氢氧化钠、氢氧化钾或氨水配制，优选浓度为0.1～2M。
所述的步骤(2)的收集液的pH优选为2～3.5，收集液加热温度优选45-55℃。
所述的步骤(3)的稀酸溶液可以是盐酸、硝酸、硫酸、磷酸等，优选盐酸；所述的酸性硒掺杂液硒含量质量百分比优选为2～7.6％；所述的酸性硒掺杂液的pH值优选控制为1～2。
所述的步骤(4)所述的乳化剂优选吐温，最终乳化剂质量百分数优选控制在0.5～2％。
所述的步骤(5)的硒掺杂酸性硅溶胶前驱物中的硅：硒的质量百分比优选为9～20：1。
所述的步骤(6)的碱性催化剂配制的碱溶液的温度优选控制在45℃～85℃，继续搅拌反应的时间为30～60min。
所述的步骤(7)的还原剂优选抗坏血酸(Vc)，溶液的温度优选控制为50℃～85℃。
本发明制备得到的可以抑制水稻重金属吸收积累生产富硒稻米的硒掺杂纳米硅溶胶稳定性高，浓度高，均一透亮，与现有技术相比，其具有以下优点：
1、通过本发明的方法制备得到的硒掺杂纳米硅溶胶，其二氧化硅含量可达20％以上，硒含量可达1％以上，且杂质含量少。
2、本发明的硒掺杂纳米硅溶胶的pH接近中性，硒以纳米颗粒分散于二氧化硅胶体中间，胶体粒径小于50纳米，在叶面喷施后，可以显著促进作物生长，抑制作物对砷的吸收积累，且增加作物硒含量，且对农作物无毒副作用，施用安全。
3、本发明的制备方法在较低的温度和常压下进行，条件温和，工艺简单，便于操作，因而易于进行大规模生产。并且其原料来源广泛，成本较低和产量较大，有利于进行推广。
附图说明：
图1是实施例1的1％硒掺杂二氧化硅溶胶扫描电镜照片；
图2是实施例1的1％硒掺杂二氧化硅溶胶粒径分布；
图3是实施例4的盆栽试验喷施不同肥料对水稻籽粒干重的影响
图4是实施例4的盆栽试验喷施不同肥料对稻米砷含量的影响；
图5是实施例4的盆栽试验喷施不同肥料对稻米硒含量的影响；
图6是实施例5的喷施不同浓度硒掺杂硅溶胶对盐鸿镇砷污染农田稻米砷含量的影响；
图7是实施例5的喷施不同浓度硒掺杂硅溶胶对盐鸿镇砷污染农田稻米硒含量的影响；
图8是实施例6的喷施不同浓度硒掺杂硅溶胶对樟市镇镉污染农田稻米镉含量的影响；
图9是实施例6的喷施不同浓度硒掺杂硅溶胶对樟市镇镉污染农田稻米硒含量的影响。
具体实施方式：
以下实施例是对本发明的进一步说明，而不是对本发明的限制。
实施例1：可以抑制水稻重金属吸收积累生产富硒稻米的硒掺杂纳米硅溶胶的制备
量取200mL水，加入1g氢氧化钠，开动搅拌器升温至55℃后，再加入250g Na2SiO3，充分溶解后冷却至室温，制得pH为12.8的金属硅酸盐溶液，金属硅酸盐的质量分数为55.5％。将上述金属硅酸盐溶液以5mL/min的速度,匀速通过100mL(湿体积)氢型强酸性阳离子多级树脂交换柱，控制柱出口收集液pH值在2～3之间，将收集液微波(或水浴)搅拌加热到50℃，静止冷却陈化30min后，得到酸性硅溶胶前驱物、备用。分别称取0.5、2.5、5、10g亚硒酸钠，溶解在50mL 0.01M的稀盐酸中，制备得到酸性硒掺杂液，其pH值为2；开动搅拌器并将酸性硒掺杂液升温至55℃后，再缓慢向酸性硒掺杂液中加入1g吐温-20；继续搅拌1小时左右，制得乳化硒掺杂液。将上述乳化硒掺杂液逐滴加到上述硒掺杂酸性硅溶胶前 驱物中，边加边搅拌，并保持温度在55℃；加完后继续搅拌30min，得到硒掺杂酸性硅溶胶前驱物。然后将该硒掺杂酸性硅溶胶前驱物缓慢加入到20毫升的浓度为25-28％的氨水中，边加边搅拌，并保持温度在45℃，滴加完毕后，其pH值在7～9之间，在45℃下继续搅拌反应30min，制得硒掺杂硅溶胶前体。将该硒掺杂硅溶胶前体液缓慢加入到经过微波(或水浴)搅拌加热到50℃的50mL 0.1M抗坏血酸(Vc)中，逐滴滴加，至溶胶淡红色不再加深，硒充分还原后，继续搅拌2小时以上，得到溶胶，所制备的溶胶经过2次渗析，并蒸发浓缩至200mL即得到均一稳定且半透明的高纯的硒掺杂纳米硅溶胶，即为本实施例的可以抑制水稻重金属吸收积累生产富硒稻米的硒掺杂纳米硅溶胶。所制得的高纯硒掺杂纳米硅溶胶中二氧化硅含量为20％，硒含量分别为0.1％、0.5％、1％和2％。图1是硒含量1％的硒掺杂纳米硅溶胶扫描电镜照片，图2是硒含量1％的硒掺杂纳米硅溶胶的粒径分布。
实施例2：可以抑制水稻重金属吸收积累生产富硒稻米的硒掺杂纳米硅溶胶的制备
量取200mL水，加入20g氢氧化钾，开动搅拌器升温至85℃后，再加入15g金属硅粉，充分溶解后冷却至室温，制得pH为13的金属硅酸盐溶液，金属硅的质量分数为6.4％。将上述金属硅酸盐溶液以5mL/min的速度,匀速通过100mL(湿体积)氢型强酸性阳离子多级树脂交换柱，控制柱出口收集液pH值在2.5～3.5之间，将收集液微波(或水浴)搅拌加热到90℃，静止冷却陈化30min后，得到酸性硅溶胶前驱物、备用。分别称取0.6、3、8、12g亚硒酸钾，溶解在50mL 0.1M的稀硝酸中，制备得到酸性硒掺杂液，其pH值为1.2；开动搅拌器并将酸性硒掺杂液升温至85℃后，再缓慢向酸性硒掺杂液中加入2.5g聚乙烯吡咯烷酮(PVP)；继续搅拌1小时左右，制得乳化硒掺杂液。将上述乳化硒掺杂液逐滴加到上述硒掺杂酸性硅溶胶前驱物中，边加边搅拌，并保持温度在85℃；加完后继续搅拌90min，得到 硒掺杂酸性硅溶胶前驱物。然后将该硒掺杂酸性硅溶胶前驱物缓慢加入到20毫升的浓度为0.5-1.2M的氢氧化钠中，边加边搅拌，并保持温度在85℃，滴加完毕后，其pH值在7～9之间，在85℃下继续搅拌反应30min，制得硒掺杂硅溶胶前体。将该硒掺杂硅溶胶前体液缓慢加入到经过微波(或水浴)搅拌加热到85℃的50mL 0.5M谷胱甘肽中，逐滴滴加，至溶胶淡红色不再加深，硒充分还原后，继续搅拌2小时以上，得到溶胶，所制备的溶胶经过2次渗析，并蒸发浓缩至200mL即得到均一稳定且半透明的高纯的硒掺杂纳米硅溶胶，即为本实施例的可以抑制水稻重金属吸收积累生产富硒稻米的硒掺杂纳米硅溶胶。所制得的高纯硒掺杂纳米硅溶胶中二氧化硅含量为15％，硒含量分别为0.12％、0.58％、1.5％和2.3％。
实施例3：可以抑制水稻重金属吸收积累生产富硒稻米的硒掺杂纳米硅溶胶的制备
量取质量分数为5％稀氨水200mL，开动搅拌器升温至35℃后，再加入50g K2SiO3，充分溶解后冷却至室温，制得pH为10.5的金属硅酸盐溶液，金属硅酸盐的质量分数为20％。将上述金属硅酸盐溶液以5mL/min的速度,匀速通过100mL(湿体积)氢型强酸性阳离子多级树脂交换柱，控制柱出口收集液pH值在2.5-3.5之间，将收集液微波(或水浴)搅拌加热到35℃，静止冷却陈化30min后，得到酸性硅溶胶前驱物、备用。分别称取0.5、1、2、4g亚硒酸氢钠，溶解在50mL 0.01M的稀流酸中，制备得到酸性硒掺杂液，其pH值为1.8；开动搅拌器并将酸性硒掺杂液升温至35℃后，再缓慢向酸性硒掺杂液中加入0.25g斯潘60；继续搅拌1小时左右，制得乳化硒掺杂液。将上述乳化硒掺杂液逐滴加到上述硒掺杂酸性硅溶胶前驱物中，边加边搅拌，并保持温度在35℃；加完后继续搅拌30min，得到硒掺杂酸性硅溶胶前驱物。然后将该硒掺杂酸性硅溶胶前驱物缓慢加入到20毫升的浓度为0.1-0.5M的氢氧化钾中，边加边搅拌，并保持温度在35℃，滴加完毕后，其pH值在7～9之间，在35℃ 下继续搅拌反应60min，制得硒掺杂硅溶胶前体。将该硒掺杂硅溶胶前体液缓慢加入到经过微波(或水浴)搅拌加热到35℃的50mL 0.1M葡萄糖中，逐滴滴加，至溶胶淡红色不再加深，硒充分还原后，继续搅拌2小时以上，得到溶胶，所制备的溶胶经过2次渗析，并蒸发浓缩至200mL即得到均一稳定且半透明的高纯的硒掺杂纳米硅溶胶，即为本实施例的可以抑制水稻重金属吸收积累生产富硒稻米的硒掺杂纳米硅溶胶。所制得的高纯硒掺杂纳米硅溶胶中二氧化硅含量为10％，硒含量分别为0.1％、0.2％、0.4％和0.8％。
实施例4：叶面喷施硒掺杂纳米硅溶胶对水稻重金属毒害缓解效果盆栽试验
供试土壤采集自广东省汕头市澄海区盐鸿镇一受砷污染水稻田，土壤取水稻田表层耕作土(0－10cm)，风干后过筛，称10公斤土装入桶内，土壤基本理化性质如下：pH6.12，有机质2.73％，全氮1.5g/kg，全磷1.02g/kg，全钾11.3g/kg，CEC 8.75cmol/kg，总砷93.6mg/kg，总硒0.879mg/kg。
水稻培育和处理：水稻品种为优优128，以5％次氯酸钠溶液对水稻种子表面消毒15分钟，用自来水冲洗后催芽、育苗，选均匀一致的幼苗进行移栽。每盆2株，在分蘖期(60－70天)时，按以下方案进行处理：(1)叶面喷施根据实施例1制备的硒掺杂纳米硅溶胶(含SiO2质量百分数为20％，含Se质量百分数为1％)，用去离子水稀释100倍后，进行叶面喷施，喷到叶面出现水珠但是不滴下为止(该处理记为1％Se-Si)；(2)叶面喷施根据我们前期发明专利(CN 101851133 B)制备的硅溶胶(含SiO2质量百分数为20％)，用去离子水稀释100倍后，进行叶面喷施，喷到叶面出现水珠但是不滴下为止(该处理记为Si)；(3)叶面喷施用市售亚硒酸钠配制的溶液(含Se质量百分数为1％)，用去离子水稀释100倍后，进行叶面喷施，喷到叶面出现水珠但是不滴下为止(该处理记为1％Se)；(4)以喷施等量的去离子 水为对照(记为CK)。每个处理重复4次，水稻成熟后收获。称取每盆稻谷干重、分析稻米中砷和硒含量。
结果如图3、4和5所示：叶面喷施硅溶胶或者实施例1的1％硒掺杂纳米硅溶胶后均可以显著促进水稻生长，水稻籽粒干重分别比对照增加了20.2％和43.8％；与叶面喷施硅溶胶相比，叶面喷施1％硒掺杂纳米硅溶胶后对水稻生长的促进作用更显著。而叶面喷施1％亚硒酸钠制备的水溶液后，对水稻生长具有抑制效应；水稻籽粒干重比对照下降了13.1％。叶面喷施硒掺杂纳米硅溶胶不仅可以促进水稻生长，而且可以抑制稻米中砷的积累，增加稻米硒含量。与对照相比，叶面喷施1％硒掺杂纳米硅溶胶后稻米砷含量下降了46％；而喷施纯硅溶胶后稻米砷含量下降了28％，喷施1％亚硒酸钠制备的水溶液后稻米砷含量下降了19％。叶面喷施1％硒掺杂纳米硅溶胶后稻米硒含量由对照的0.050mg/kg增加到0.272mg/kg；达到了富硒大米标准。而叶面喷施1％亚硒酸钠制备的水溶液后稻米硒含量为0.180mg/kg；仅为叶面喷施1％硒掺杂纳米硅溶胶稻米的66％。因此，用本专利所生产的硒掺杂纳米硅溶胶对水稻进行叶面喷施后，可以进一步提升叶面硅肥抑制水稻砷吸收的效果，同时可以生产出富硒大米；且比直接喷施亚硒酸钠安全高效。
实施例5：叶面喷施硒掺杂纳米硅溶胶降低水稻重金属砷吸收大田实验效果
实施地点：广东省汕头市澄海区盐鸿镇一受砷污染水稻田，土壤基本理化性质如下：pH6.12，，总砷93.6mg/kg，总硒0.879mg/kg。水稻品种为培杂双七.
大田水稻叶面喷施硒掺杂纳米硅溶胶的方法：
(1)喷施时间：在水稻分蘖期(大约60天左右)，选择晴天或多云天气的午后4点左右，进行喷施；如喷后24小时内下雨，则补喷一次。
(2)喷施的浓度和剂量：用实施例1所生产的系列浓度梯度的硒掺杂纳米硅溶胶，其含硅量为20％，含硒量分别为0.1％、0.5％、1％和2％，每亩用量约1L，兑水100L进行叶面喷施；以喷施等量的清水为对照；分别记为0.1％Se-Si、0.5％Se-Si、1％Se-Si、2％Se-Si、CK。每个处理4个小区，随机区组排列。
(3)田间管理：和普通水稻田间管理一样。水稻成熟后收获，分析每个小区稻米镉和硒含量。
结果如图6和7所示：在盐鸿镇的大田试验证实叶面喷施不同浓度硒掺杂纳米硅溶胶后，均可以显著抑制稻米对砷的吸收积累，且增加稻米硒含量；随着硒掺杂量的增加，稻米硒含量显著增加，而稻米砷含量则显著下降。与对照相比，叶面分别喷施0.1％、0.5％、1％和2％的硒掺杂纳米硅溶胶后，稻米砷含量分别下降了19.1％、45.9％、59.4％和63.7％；而稻米硒含量则分别增加了67.5％、265％、443％和631％。其中当硒掺杂浓度达到0.5％时，稻米砷含量符合国家食品安全标准(无机砷<0.2mg/kg GB2762—2012)；而当硒掺杂量为0.1％和0.5％时，稻米中硒的含量分别为0.12mg/kg和0.26mg/kg，符合富硒大米标准。因此，在盐鸿镇通过叶面喷施含0.5％硒掺杂纳米硅溶胶，可以在砷污染农田上生产出砷含量达标的富硒大米。
实施例6：叶面喷施硒掺杂纳米硅溶胶降低水稻重金属镉砷吸收大田实验效果
实施地点：广东省韶关市曲江区樟市镇一受镉污染农田；农田土壤pH为5.32，总Cd含量为0.905mg/kg，总硒含量为0.512mg/kg。水稻品种为美香。
大田水稻叶面喷施实施例1制备的硒掺杂纳米硅溶胶的方法：同实施例7
结果如图8和9所示：在樟市镇的大田试验证实叶面喷施不同浓度硒掺杂纳米硅溶胶后，均可以显著抑制稻米对镉的吸收积累，且增加稻米硒含量；随着硒掺杂量的增加，稻米硒含 量显著增加，而稻米镉含量则显著下降。与对照相比，叶面分别喷施0.1％、0.5％、1％和2％的硒掺杂纳米硅溶胶后，稻米镉含量分别下降了37.5％、44.4％、63.9％和79.6％；而稻米硒含量则分别增加了80.7％、288％、600％和778％。其中当硒掺杂浓度达到1％时，稻米镉含量下降到0.2mg/kg以下，符合国家食品安全标准(镉<0.2mg/kg GB 2762—2012)；而当硒掺杂量为0.5％和1％时，稻米中硒的含量分别为0.16mg/kg和0.28mg/kg；符合富硒大米标准。因此，在樟市镇通过叶面喷施含1％硒掺杂纳米硅溶胶，可以在镉污染农田上生产出镉含量达标的富硒大米。

Claims (9)

  1. 一种可以抑制水稻重金属吸收积累生产富硒稻米的硒掺杂纳米硅溶胶的制备方法，其特征在于，包括以下步骤：
    (1)配制金属硅酸盐溶液：将金属硅粉或金属硅酸盐在搅拌条件加入到浓度为0.1～5M的碱性溶液中，配制成金属硅酸盐溶液，其中含的金属硅粉或金属硅酸盐的浓度为重量百分比5％至饱和，pH为10～13；所述的金属硅酸盐为Na2SiO3、K2SiO3或Li2SiO3；
    (2)制备酸性硅溶胶前驱物：将金属硅酸盐溶液经过阳离子交换处理，控制收集液pH为1～4，将收集液加热到35-90℃，再静止冷却陈化，得到酸性硅溶胶前驱物；
    (3)制备酸性硒掺杂液：将含硒化合物在搅拌条件下溶解到稀酸溶液中，制备硒含量质量百分比为0.1-10％的酸性硒掺杂液，酸性硒掺杂液的pH值控制为1～4；所述的含硒化合物为亚硒酸、亚硒酸钠、亚硒酸钾或者亚硒酸氢钠；
    (4)制备乳化硒掺杂液：在搅拌条件下，将乳化剂加入到步骤(3)的酸性硒掺杂液中，最终乳化剂质量百分数控制在0.05～5％，由此得到乳化硒掺杂液；所述的乳化剂为聚乙烯吡咯烷酮、聚乙烯醇、吐温系列或斯潘系列；
    (5)制备硒掺杂酸性硅溶胶前驱物：将步骤(4)的乳化硒掺杂液在搅拌条件下加入到步骤(2)的酸性硅溶胶前驱物中，得到硒掺杂酸性硅溶胶前驱物，其中硒掺杂酸性硅溶胶前驱物中的硅：硒的质量百分比为3～200：1；
    (6)将步骤(5)的硒掺杂酸性硅溶胶前驱物加入到30℃～90℃的碱性催化剂配制的碱溶液中，直至碱溶液的pH值到7～9之时停止加入，继续搅拌反应30～90min，得到硒掺杂硅溶胶前体；所述的碱性催化剂为氢氧化钠、氢氧化钾、尿素、氨水或者硅酸钠溶液；
    (7)将步骤(6)的硒掺杂硅溶胶前体加入到30℃～90℃的还原剂溶液中，直至溶胶淡 红色不再加深，硒充分还原后，继续搅拌反应2小时以上，然后再经2次以上渗析，即得到硒掺杂纳米硅溶胶；所述的还原剂为抗坏血酸、谷胱甘肽或还原性糖类。
  2. 根据权利要求1所述的制备方法，其特征在于，所述的步骤(1)的碱性溶液是用氢氧化钠、氢氧化钾或氨水配制，浓度为0.1～2M。
  3. 根据权利要求1所述的制备方法，其特征在于，所述的步骤(2)的收集液的pH为2～3.5，收集液加热到温度45-55℃。
  4. 根据权利要求1所述的制备方法，其特征在于，所述的步骤(3)的稀酸溶液是稀盐酸、稀硝酸、稀硫酸或稀磷酸溶液；所述的酸性硒掺杂液硒含量质量百分比为2～7.6％；所述的酸性硒掺杂液的pH值控制为1～2。
  5. 根据权利要求1所述的制备方法，其特征在于，所述的步骤(4)所述的乳化剂为吐温，最终乳化剂质量百分数控制在0.5～2％。
  6. 根据权利要求1所述的制备方法，其特征在于，所述的步骤(5)的硒掺杂酸性硅溶胶前驱物中的硅：硒的质量百分比为9～20：1。
  7. 根据权利要求1所述的制备方法，其特征在于，所述的步骤(6)的碱性催化剂配制的碱溶液的温度控制在45℃～85℃，继续搅拌反应的时间为30～60min。
  8. 根据权利要求1所述的制备方法，其特征在于，所述的步骤(7)的还原剂为抗坏血酸，溶液的温度控制为50℃～85℃。
  9. 一种根据权利要求1、2、3、4、5、6、7或8所述的制备方法制备得到的可以抑制水稻重金属吸收积累生产富硒稻米的硒掺杂纳米硅溶胶。
PCT/CN2014/088288 2013-12-26 2014-10-10 一种可以抑制水稻重金属吸收积累生产富硒稻米的硒掺杂纳米硅溶胶及其制备方法 WO2015096533A1 (zh)

Priority Applications (2)

Application Number Priority Date Filing Date Title
JP2015554051A JP6068679B2 (ja) 2013-12-26 2014-10-10 水稲重金属の吸収と蓄積を抑制でき、且つ高セレン含有米を生産できるセレンドープナノシリカゾルの調製方法
US14/771,189 US9919978B2 (en) 2013-12-26 2014-10-10 Selenium-doped nano silica sol used for producing selenium-enriched rice and capable of suppressing absorption and accumulation of heavy metals in paddy rice and preparation method therefor

Applications Claiming Priority (2)

Application Number Priority Date Filing Date Title
CN201310737996.X 2013-12-26
CN201310737996.XA CN103789114B (zh) 2013-12-26 2013-12-26 一种可以抑制水稻重金属吸收积累生产富硒稻米的硒掺杂纳米硅溶胶及其制备方法

Publications (1)

Publication Number Publication Date
WO2015096533A1 true WO2015096533A1 (zh) 2015-07-02

Family

ID=50665176

Family Applications (1)

Application Number Title Priority Date Filing Date
PCT/CN2014/088288 WO2015096533A1 (zh) 2013-12-26 2014-10-10 一种可以抑制水稻重金属吸收积累生产富硒稻米的硒掺杂纳米硅溶胶及其制备方法

Country Status (4)

Country Link
US (1) US9919978B2 (zh)
JP (1) JP6068679B2 (zh)
CN (1) CN103789114B (zh)
WO (1) WO2015096533A1 (zh)

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN105347972A (zh) * 2015-12-14 2016-02-24 丽水学院 以介孔氧化硅为重金属钝化剂和微生物载体的堆肥方法
JP2018512840A (ja) * 2016-03-02 2018-05-24 広東省生態環境技術研究所Ｇｕａｎｇｄｏｎｇ Ｉｎｓｔｉｔｕｔｅ Ｏｆ Ｅｃｏ−Ｅｎｖｉｒｏｎｍｅｎｔａｌ Ｓｃｉｅｎｃｅ ＆ Ｔｅｃｈｎｏｌｏｇｙ 水稲におけるカドミウムの吸収及び輸送に関連する遺伝子の発現を正確にコントロールする葉面ブロッキング剤及びその応用
CN114190131A (zh) * 2021-12-25 2022-03-18 西北农林科技大学 一种番茄专用富硒硅叶面喷施剂及其制备方法和应用
CN114276184A (zh) * 2021-09-05 2022-04-05 江苏中农科食品工程股份有限公司 一种缓释硒材料的制备方法及应用

Families Citing this family (30)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN103789114B (zh) * 2013-12-26 2015-08-26 广东省生态环境与土壤研究所 一种可以抑制水稻重金属吸收积累生产富硒稻米的硒掺杂纳米硅溶胶及其制备方法
CN105733592A (zh) * 2016-02-02 2016-07-06 深圳百乐宝生物农业科技有限公司 一种降低重金属活性的土壤调理剂及用途
CN106105926A (zh) * 2016-06-28 2016-11-16 华南农业大学 一种降低高浓度镉污染下水稻籽粒镉含量的施硅方法
CN106561710B (zh) * 2016-11-08 2018-05-15 佛山市铁人环保科技有限公司 一种可降解农残的二氧化钛溶胶及其制备方法
CN106631366B (zh) * 2016-11-08 2018-06-26 佛山市铁人环保科技有限公司 一种富硒降镉叶面硅肥及其制备方法和应用
CN106495900B (zh) * 2016-11-09 2020-02-21 环保桥（湖南）生态环境修复有限公司 一种用于抑制水稻和蔬菜富集重金属的掺杂硒含硅富硫叶面阻控剂及其制备方法
CN107087638B (zh) * 2017-03-10 2019-05-07 浙江大学 降低水稻籽粒中砷含量的制剂及其制备法和用法
CN106927949A (zh) * 2017-03-21 2017-07-07 广东省生态环境技术研究所 一种用于降解农产品中农药及重金属的硒掺杂纳米钛溶胶及其制备方法和应用
CN107935729A (zh) * 2017-12-21 2018-04-20 武汉雅酷硒纳米生物技术有限公司 一种纳米硒水肥溶液及其制备方法
CN108713367A (zh) * 2018-04-28 2018-10-30 湖北夷枝红富硒生物科技有限公司 一种富硒大米的水稻施肥方法
IT201800005413A1 (it) * 2018-05-16 2019-11-16 Cereali arricchiti
CN108967442B (zh) * 2018-07-24 2020-06-05 广东省生态环境技术研究所 一种抑制水稻镉砷积累的亚铁改性硒溶胶及其制备方法与应用
CN109122136B (zh) 2018-07-24 2021-03-23 广东省科学院生态环境与土壤研究所 一种中轻度重金属污染土壤上稻米安全生产的方法
RO133904B1 (ro) * 2018-08-28 2023-11-29 Institutul Naţional De Cercetare Dezvoltare Pentru Chimie Şi Petrochimie - Icechim Bucureşti Procedeu de obţinere a suspensiilor stabile de nanoparticule de seleniu şi silice
CN109384239A (zh) * 2018-10-29 2019-02-26 佛山市铁人环保科技有限公司 一种硒锌掺杂二氧化硅复合溶胶及其制备方法和应用
CN109588235B (zh) * 2018-11-08 2021-12-21 暨南大学 多糖功能化纳米硒在富硒水稻种植中的应用
CN109729963A (zh) * 2019-02-01 2019-05-10 佛山科学技术学院 一种基于水稻材料的纳米硅沉积阻隔重金属方法
CN109892185A (zh) * 2019-04-01 2019-06-18 淮南师范学院 一种叶面阻抑水稻籽粒镉积累的种植方法
CN110934152B (zh) * 2019-12-11 2021-06-15 浙江大学 一种降低水稻籽粒中镉砷含量的浸种剂及浸种方法
EP4098105A4 (en) * 2020-01-28 2024-02-21 Yoon Young Gang METHOD FOR CULTIVATING FUNCTIONAL CROPS USING NANO-ORGANIC GERMANIUM AND NANO-ORGANIC SELENIUM
CN111819946B (zh) * 2020-07-30 2022-09-20 上海绿乐生物科技有限公司 一种稻田土壤生态环境的综合改良方法
CN113461451A (zh) * 2020-09-04 2021-10-01 达州市土壤肥料与生态建设工作站 一种含硒有机水溶生物肥及其制备方法
CN112299888B (zh) * 2020-11-19 2022-09-30 杭州富春硒谷农业科技有限公司 一种纳米硒营养液及其制备方法
GB2610456A (en) * 2021-01-15 2023-03-08 Inst Soil Science Cas Simplified method for reducing cadmium of rice and use thereof
CN113149776A (zh) * 2021-03-31 2021-07-23 海南自贸区沃佳实业有限公司 一种富硒有机肥及其制备方法
CN113020250B (zh) * 2021-04-07 2022-12-09 淮南师范学院 生产低镉稻米同时修复稻田土壤镉污染的方法
CN113261485A (zh) * 2021-05-24 2021-08-17 中国科学院南京土壤研究所 一种降低稻米镉含量的轻简化方法及应用
CN114031461B (zh) * 2021-10-26 2023-07-14 中冶南方都市环保工程技术股份有限公司 一种用于降低稻米中铬和砷含量的有机硅肥及其制备方法和应用
CN114711112B (zh) * 2022-04-18 2023-06-13 江南大学 一种增加分蘖来提高富硒水稻产量的方法
CN115160065B (zh) * 2022-07-22 2023-06-27 环保桥(湖南)生态环境工程股份有限公司 一种用于水稻富硒降镉降砷叶面阻控剂及其制备方法

Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1789113A (zh) * 2004-12-17 2006-06-21 宁波大学 一种纳米硒溶胶的制备方法
CN1907029A (zh) * 2006-08-09 2007-02-07 广东省生态环境与土壤研究所 一种可抑制水稻吸收重金属的稀土复合硅溶胶
CN101851133A (zh) * 2010-04-27 2010-10-06 广东省生态环境与土壤研究所 一种叶面硅肥的制备方法及其使用方法
WO2013039479A1 (en) * 2011-09-13 2013-03-21 Empire Technology Development Llc Nanosorbents and methods of use thereof
CN103789114A (zh) * 2013-12-26 2014-05-14 广东省生态环境与土壤研究所 一种可以抑制水稻重金属吸收积累生产富硒稻米的硒掺杂纳米硅溶胶及其制备方法

Family Cites Families (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US20040091417A1 (en) * 2002-11-07 2004-05-13 Nanoproducts Corporation Nanotechnology for agriculture, horticulture, and pet care
EP1570715A1 (en) * 2004-03-02 2005-09-07 Eurochem N.V. Seed pellets and soils for growing plants
ATE486930T1 (de) * 2004-06-07 2010-11-15 Sampath Kumar Thothathri Wachstumsfördernde zusammensetzung für kieselalgen
WO2009127256A1 (en) * 2008-04-17 2009-10-22 Jisbrey, S.A Hydronium stabilized and dissoluble silicic acid nanoparticles: preparation, stabilization and use
EP3262937A1 (en) * 2009-12-09 2018-01-03 Barlaa B.V. Micro-colloidal silicic acid composition
CN101830735B (zh) 2010-04-27 2012-05-30 广东省生态环境与土壤研究所 一种用于降低蔬菜重金属和硝酸盐含量的复合叶面硅肥及其制备方法

Patent Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1789113A (zh) * 2004-12-17 2006-06-21 宁波大学 一种纳米硒溶胶的制备方法
CN1907029A (zh) * 2006-08-09 2007-02-07 广东省生态环境与土壤研究所 一种可抑制水稻吸收重金属的稀土复合硅溶胶
CN101851133A (zh) * 2010-04-27 2010-10-06 广东省生态环境与土壤研究所 一种叶面硅肥的制备方法及其使用方法
WO2013039479A1 (en) * 2011-09-13 2013-03-21 Empire Technology Development Llc Nanosorbents and methods of use thereof
CN103789114A (zh) * 2013-12-26 2014-05-14 广东省生态环境与土壤研究所 一种可以抑制水稻重金属吸收积累生产富硒稻米的硒掺杂纳米硅溶胶及其制备方法

Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN105347972A (zh) * 2015-12-14 2016-02-24 丽水学院 以介孔氧化硅为重金属钝化剂和微生物载体的堆肥方法
CN105347972B (zh) * 2015-12-14 2018-11-06 丽水学院 以介孔氧化硅为重金属钝化剂和微生物载体的堆肥方法
JP2018512840A (ja) * 2016-03-02 2018-05-24 広東省生態環境技術研究所Ｇｕａｎｇｄｏｎｇ Ｉｎｓｔｉｔｕｔｅ Ｏｆ Ｅｃｏ−Ｅｎｖｉｒｏｎｍｅｎｔａｌ Ｓｃｉｅｎｃｅ ＆ Ｔｅｃｈｎｏｌｏｇｙ 水稲におけるカドミウムの吸収及び輸送に関連する遺伝子の発現を正確にコントロールする葉面ブロッキング剤及びその応用
US10420291B2 (en) * 2016-03-02 2019-09-24 Guangdong Institute Of Eco-Environmental Science & Technology Foliage blocking agent for precise regulation of expression of cadmium absorption and transportation-related gene in rice and application thereof
CN114276184A (zh) * 2021-09-05 2022-04-05 江苏中农科食品工程股份有限公司 一种缓释硒材料的制备方法及应用
CN114190131A (zh) * 2021-12-25 2022-03-18 西北农林科技大学 一种番茄专用富硒硅叶面喷施剂及其制备方法和应用

Also Published As

Publication number Publication date
CN103789114A (zh) 2014-05-14
US9919978B2 (en) 2018-03-20
US20160289129A1 (en) 2016-10-06
JP2016511232A (ja) 2016-04-14
CN103789114B (zh) 2015-08-26
JP6068679B2 (ja) 2017-01-25

Similar Documents

Publication Publication Date Title
WO2015096533A1 (zh) 一种可以抑制水稻重金属吸收积累生产富硒稻米的硒掺杂纳米硅溶胶及其制备方法
US10633588B2 (en) Preparation and use of slow-release iron-based biochar soil heavy metal passivator
CN109122136B (zh) 一种中轻度重金属污染土壤上稻米安全生产的方法
CN106631366B (zh) 一种富硒降镉叶面硅肥及其制备方法和应用
JP5374647B2 (ja) 野菜における重金属および硝酸塩の含有量を低減するために用いられる葉面複合ケイ素肥料とその調製方法
CN103204734B (zh) 纳米稀土硒硅钛宏微量元素复合营养肥
CN1330611C (zh) 果蔬类纳米硒营养调节剂及其制备方法
CN104447021A (zh) 一种采用混合菌液发酵制备的富硒微生物制剂及制备方法
CN103814720B (zh) 一种低硒茶园降低土壤有机污染并生产富硒茶的方法
CN104276892A (zh) 一种毛竹笋富硒专用液态肥及其制备方法
CN102173906A (zh) 一种无土栽培营养液及其制备方法和应用
CN105418193A (zh) 一种沼液沼渣为原料发酵制备的富硒生物制剂及制备方法
CN107473909A (zh) 一种具有防控病虫害功能的有机无机复合肥及其制备方法
CN106747680A (zh) 一种碱法活化煤矸石中活性元素硒及其硒肥的制备方法
CN105130586A (zh) 一种糖醇螯合纳米有机硒肥料及其制备方法
CN103011973A (zh) 一种具有缓释控失效果的增效型氮磷钾复合肥的制造方法
CN102771295A (zh) 一种提高茶树对硒肥吸收效率的方法
CN115784790A (zh) 一种植物用锌硒营养液及其制备方法和应用
CN102771296A (zh) 一种提高水稻对含硒肥料吸收利用率的方法
CN102050649A (zh) 腐殖酸花卉营养液
CN105110878A (zh) 一种纳米化肥农药增效剂及其制备方法
CN103086794A (zh) 一种富硒土壤营养剂及其配制方法、黄山贡菊的栽培方法
CN102150590A (zh) 富有机硒无花果及其生产方法
CN113860948A (zh) 一种水溶性有机纳米悬浮硅液体肥料及其制备方法和应用
CN105347997A (zh) 一种腐植酸硅硒肥料及其制备工艺

Legal Events

Date Code Title Description
ENP Entry into the national phase

Ref document number: 2015554051

Country of ref document: JP

Kind code of ref document: A

121 Ep: the epo has been informed by wipo that ep was designated in this application

Ref document number: 14875746

Country of ref document: EP

Kind code of ref document: A1

WWE Wipo information: entry into national phase

Ref document number: 14771189

Country of ref document: US

NENP Non-entry into the national phase

Ref country code: DE

122 Ep: pct application non-entry in european phase

Ref document number: 14875746

Country of ref document: EP

Kind code of ref document: A1