脫落酸光降解機(jī)理、穩(wěn)定方法及其生理效應(yīng)評價(jià)
[Abstract]:Abscisic acid (ABA) is an important plant hormone that regulates plant growth, signal transduction and plant immune defense. Exogenous application of ABA has many functions such as prolonging florescence, increasing fruit coloring rate and improving crop drought resistance. However, under light, ABA can easily degrade deactivation and greatly reduce its use effect. Moreover, ABA There are few reports on photodegradation and photostabilization methods. This study established the kinetic equation of ABA photodegradation, and studied the effect of different environmental factors on the degradation of ABA photodegradation according to the equation. The degradation products of ABA were analyzed by HPLC-MS/MS, and the photodegradation mechanism of ABA was further clarified. The photodegradation mechanism of ABA was studied according to the photodegradation mechanism of ABA. In order to reduce the effect of ABA photodegradation, the combination of ABA and hexanoate two ethanolates was synthesized. This study provides theoretical guidance for explaining the mechanism of ABA photodegradation, developing photostable products and production applications. The main results are as follows: 1. under ultraviolet radiation, ABA follows an approximate 50% isomerization to trans-ABA, and then with the generated trans-ABA In the buffer system with pH 8, the rate constant of ABA isomerization is 0.0466 min-1, the equilibrium time is 55 mmin, and the further attenuating half-life is 506min, 94% and 41 times and 40 times the.ABA concentration of 280 mg/l, respectively, when pH is 3, respectively. The rate constant of isomerization is 0.0182min-1, the equilibrium time is 58min, the further attenuating half-life is 521min, which is 96% smaller than that of 5mg/l, and the rate constant of.ABA photoisomerization is nearly 17 times and 10 times higher than that at 10. The rate constant of the isomerization is not obviously different from that at 22. The rate constant of the isomerization is slightly decreased at 40 C, and the difference is significant. After 40.7 hours of visible light irradiation, the residual ABA was 98%, while the ABA in the unpurplish control was nearly degraded by 4.5 times faster than that under the high pressure mercury lamp, 4.5 times faster than that under the xenon light lamp, the balance time accelerated by 76%, and the further attenuating half-life accelerated by 62%, which could be caused by the ultraviolet intensity of the mercury lamp was 20 times higher than that of the latter. It can be concluded that light does not affect the photodegradation of ABA; ultraviolet light is the main cause of the degradation of ABA and is positively related to the strength; the ABA of the anionic form helps to slow down its degradation; the high concentration ABA degradation is slow when the pH and ultraviolet radiation intensity is certain, and the increase of temperature within the range of 10-40 degrees does not accelerate the photodegradation of.2. based on ABA. 4 main products of ABA attenuation period were found by liquid chromatography and mass spectrogram of mass spectrometry. The components of each component were analyzed by UV total sweep and first order two mass spectrometry, combined with trans-ABA, ABA standard atlas. It was found that 4-trans-3-methylene ABA was mainly produced in the decay period, except for the generated trans-ABA, 4. -cis-3-methylene ABA and other ABA isomers. Therefore, combined with the result 1, it can be concluded that the photodegradation mechanism of ABA is: under UV irradiation, ABA isomerization to trans-ABA, then 4-trans-3-methylene ABA, 4-cis-3-methyleneABA and so on, and the decrease of ABA concentration and pH value, and the enhancement of UV intensity will accelerate the solubility of water solubility of ABA. UV Absorbents 2- hydroxyl 4- methoxy -5- sulfonic acid two benzophenone (BP-4) and oil soluble UV Absorbents 2- hydroxyl -4- oxo benzophenone (UV-531) significantly reduced the photodegradation of ABA, and there was no significant difference between the two. The light stabilizer double (2,2,6,6- four methyl -4- piperidine) sebacate (HS-770) accelerated the photodegradation of ABA, and did not strengthen The effect. After 2 hours of UV irradiation with 200 mg/1 BP-4, the residual ratio of ABA was 26% more than that of ABA control. The inhibitory activity of 300 times dilution of the solution on wheat seed (Jimmy 22) bud and root elongation was more than 13% higher than that of a control diluent only containing ABA. Therefore, it was concluded that a water-soluble UV absorber BP-4 is a kind. The high efficiency additive.4. can significantly increase the stability of ABA under UV, 280 mg/1 ABA with 2000 mg/1 lignosulfonate Ufoxane 3A after UV irradiation for 2 hours, and ABA remaining 92%, but only ABA control remaining 40%. The inhibitory activity of the 300 times diluent on the malt and root elongation is nearly 20% higher than that of a control diluent containing ABA only. Other kinds of lignosulfonate have no significant difference in ABA light stabilization effect compared with Ufoxane 3A. When.Ufoxane 3A is at 2000 mg/1 and below the concentration, there is no stress effect and biological activity on the germination and growth of wheat seeds compared with clear water. Therefore, it can be concluded that lignosulfonate can significantly improve ABA in purple. In addition to the additives for the stability of the outside, and because of innocuity and harmlessness, they can be biodegraded and they can be maintained at a high dosage to achieve the optimal effect of.5. synthesis of ABA and hexanoate two ethanolate complex by NMR and the stability of the coordination ratio of 1/1. complex in ultraviolet light is significantly higher than that of pH in the buffer system of 6 and below. ABA inhibited the germination of wheat seeds by 13% higher than that of ABA, and showed better plant growth regulating activity.
【學(xué)位授予單位】:中國農(nóng)業(yè)大學(xué)
【學(xué)位級別】:博士
【學(xué)位授予年份】:2016
【分類號】:Q945
【相似文獻(xiàn)】
相關(guān)期刊論文 前10條
1 席國喜,宋世理,劉琴;硫酸鹽存在下廢有機(jī)玻璃熱降解機(jī)理的探討[J];河南師范大學(xué)學(xué)報(bào)(自然科學(xué)版);2005年02期
2 紀(jì)樹蘭,鄧麗萍,鄭大威,任海燕,彭躍蓮;可動(dòng)苯基桿菌對LAS生物降解機(jī)理的初步探討[J];北京工業(yè)大學(xué)學(xué)報(bào);2003年02期
3 張錫輝,白志俳;難降解有機(jī)污染物共降解機(jī)理解析[J];上海環(huán)境科學(xué);2000年07期
4 薛立娟,張文嵐,劉莉,王維忠;p53蛋白的降解機(jī)理[J];白求恩醫(yī)科大學(xué)學(xué)報(bào);1998年06期
5 鄧克儉,羅俊華;AM1分析喹諾酮類藥物的熱降解機(jī)理[J];中南民族大學(xué)學(xué)報(bào)(自然科學(xué)版);2003年01期
6 張敏;王曉霞;劉保健;劉曉霞;王蕾;邱建輝;;生物可降解脂肪族聚酯在陜西土壤中的降解行為[J];高分子材料科學(xué)與工程;2008年01期
7 楊林;薛罡;劉亞男;;卡馬西平降解菌的篩選分離及其降解機(jī)理[J];環(huán)境工程學(xué)報(bào);2012年05期
8 周生輝;王菲鳳;李青松;陳幼華;高乃云;;KMnO_4-PAC聯(lián)用工藝去除水中三氯生及其降解機(jī)理研究[J];福建師范大學(xué)學(xué)報(bào)(自然科學(xué)版);2013年06期
9 吳獻(xiàn)花,孫s釷,
本文編號:2154760
本文鏈接:http://sikaile.net/shoufeilunwen/jckxbs/2154760.html