CN114333988A - Estimation method for the contribution rate of plant β-CAS and ST to KCN metabolism - Google Patents
Estimation method for the contribution rate of plant β-CAS and ST to KCN metabolism Download PDFInfo
- Publication number
- CN114333988A CN114333988A CN202111383400.1A CN202111383400A CN114333988A CN 114333988 A CN114333988 A CN 114333988A CN 202111383400 A CN202111383400 A CN 202111383400A CN 114333988 A CN114333988 A CN 114333988A
- Authority
- CN
- China
- Prior art keywords
- kcn
- plant
- metabolism
- treatment group
- cas
- Prior art date
- Legal status (The legal status 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 status listed.)
- Pending
Links
- 230000004060 metabolic process Effects 0.000 title claims description 109
- 238000000034 method Methods 0.000 title claims description 31
- 241000196324 Embryophyta Species 0.000 claims description 136
- 235000015097 nutrients Nutrition 0.000 claims description 42
- 108090000623 proteins and genes Proteins 0.000 claims description 23
- 230000002503 metabolic effect Effects 0.000 claims description 21
- 230000014509 gene expression Effects 0.000 claims description 20
- 238000006243 chemical reaction Methods 0.000 claims description 11
- 238000004364 calculation method Methods 0.000 claims description 10
- 230000005068 transpiration Effects 0.000 claims description 9
- 230000001186 cumulative effect Effects 0.000 claims description 8
- 238000012937 correction Methods 0.000 claims description 6
- 230000001105 regulatory effect Effects 0.000 claims description 6
- 230000008859 change Effects 0.000 claims description 3
- 208000020990 adrenal cortex carcinoma Diseases 0.000 claims 9
- 241000209094 Oryza Species 0.000 description 106
- 235000007164 Oryza sativa Nutrition 0.000 description 106
- 235000009566 rice Nutrition 0.000 description 106
- PAJPWUMXBYXFCZ-UHFFFAOYSA-N 1-aminocyclopropanecarboxylic acid Chemical compound OC(=O)C1(N)CC1 PAJPWUMXBYXFCZ-UHFFFAOYSA-N 0.000 description 46
- 239000000243 solution Substances 0.000 description 45
- HEMHJVSKTPXQMS-UHFFFAOYSA-M Sodium hydroxide Chemical compound [OH-].[Na+] HEMHJVSKTPXQMS-UHFFFAOYSA-M 0.000 description 9
- 238000004458 analytical method Methods 0.000 description 8
- TWBYWOBDOCUKOW-UHFFFAOYSA-N isonicotinic acid Chemical compound OC(=O)C1=CC=NC=C1 TWBYWOBDOCUKOW-UHFFFAOYSA-N 0.000 description 8
- 238000010586 diagram Methods 0.000 description 7
- 230000008569 process Effects 0.000 description 6
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 6
- 238000011156 evaluation Methods 0.000 description 5
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 description 4
- 238000011529 RT qPCR Methods 0.000 description 4
- 238000004821 distillation Methods 0.000 description 4
- 238000002474 experimental method Methods 0.000 description 4
- 230000008439 repair process Effects 0.000 description 4
- 238000004088 simulation Methods 0.000 description 4
- 241000219194 Arabidopsis Species 0.000 description 3
- ZMXDDKWLCZADIW-UHFFFAOYSA-N N,N-Dimethylformamide Chemical compound CN(C)C=O ZMXDDKWLCZADIW-UHFFFAOYSA-N 0.000 description 3
- 238000009825 accumulation Methods 0.000 description 3
- 230000009286 beneficial effect Effects 0.000 description 3
- 239000003153 chemical reaction reagent Substances 0.000 description 3
- KRKNYBCHXYNGOX-UHFFFAOYSA-N citric acid Chemical compound OC(=O)CC(O)(C(O)=O)CC(O)=O KRKNYBCHXYNGOX-UHFFFAOYSA-N 0.000 description 3
- 238000001727 in vivo Methods 0.000 description 3
- 239000007788 liquid Substances 0.000 description 3
- 238000004519 manufacturing process Methods 0.000 description 3
- 238000002156 mixing Methods 0.000 description 3
- JEXVQSWXXUJEMA-UHFFFAOYSA-N pyrazol-3-one Chemical compound O=C1C=CN=N1 JEXVQSWXXUJEMA-UHFFFAOYSA-N 0.000 description 3
- 239000000126 substance Substances 0.000 description 3
- DCXYFEDJOCDNAF-UHFFFAOYSA-N Asparagine Chemical compound OC(=O)C(N)CC(N)=O DCXYFEDJOCDNAF-UHFFFAOYSA-N 0.000 description 2
- NBIIXXVUZAFLBC-UHFFFAOYSA-N Phosphoric acid Chemical compound OP(O)(O)=O NBIIXXVUZAFLBC-UHFFFAOYSA-N 0.000 description 2
- 238000010521 absorption reaction Methods 0.000 description 2
- 230000015572 biosynthetic process Effects 0.000 description 2
- 238000013461 design Methods 0.000 description 2
- 238000001514 detection method Methods 0.000 description 2
- 239000003344 environmental pollutant Substances 0.000 description 2
- 238000012854 evaluation process Methods 0.000 description 2
- 239000000463 material Substances 0.000 description 2
- 230000037353 metabolic pathway Effects 0.000 description 2
- 238000005065 mining Methods 0.000 description 2
- 229910052757 nitrogen Inorganic materials 0.000 description 2
- 231100000719 pollutant Toxicity 0.000 description 2
- 238000012797 qualification Methods 0.000 description 2
- 239000002689 soil Substances 0.000 description 2
- 239000006228 supernatant Substances 0.000 description 2
- 238000003786 synthesis reaction Methods 0.000 description 2
- 238000012360 testing method Methods 0.000 description 2
- 238000012546 transfer Methods 0.000 description 2
- BXRLWGXPSRYJDZ-UHFFFAOYSA-N 3-cyanoalanine Chemical compound OC(=O)C(N)CC#N BXRLWGXPSRYJDZ-UHFFFAOYSA-N 0.000 description 1
- 101000697822 Arabidopsis thaliana Thiosulfate/3-mercaptopyruvate sulfurtransferase 1, mitochondrial Proteins 0.000 description 1
- 101000628698 Arabidopsis thaliana Thiosulfate/3-mercaptopyruvate sulfurtransferase 2 Proteins 0.000 description 1
- XFXPMWWXUTWYJX-UHFFFAOYSA-N Cyanide Chemical compound N#[C-] XFXPMWWXUTWYJX-UHFFFAOYSA-N 0.000 description 1
- 108020004414 DNA Proteins 0.000 description 1
- 102000007260 Deoxyribonuclease I Human genes 0.000 description 1
- 108010008532 Deoxyribonuclease I Proteins 0.000 description 1
- KCXVZYZYPLLWCC-UHFFFAOYSA-N EDTA Chemical compound OC(=O)CN(CC(O)=O)CCN(CC(O)=O)CC(O)=O KCXVZYZYPLLWCC-UHFFFAOYSA-N 0.000 description 1
- 108090000790 Enzymes Proteins 0.000 description 1
- 102000004190 Enzymes Human genes 0.000 description 1
- VGGSQFUCUMXWEO-UHFFFAOYSA-N Ethene Chemical compound C=C VGGSQFUCUMXWEO-UHFFFAOYSA-N 0.000 description 1
- 239000005977 Ethylene Substances 0.000 description 1
- 108091092584 GDNA Proteins 0.000 description 1
- CKLJMWTZIZZHCS-REOHCLBHSA-N L-aspartic acid Chemical compound OC(=O)[C@@H](N)CC(O)=O CKLJMWTZIZZHCS-REOHCLBHSA-N 0.000 description 1
- 240000003183 Manihot esculenta Species 0.000 description 1
- 235000016735 Manihot esculenta subsp esculenta Nutrition 0.000 description 1
- 102000004316 Oxidoreductases Human genes 0.000 description 1
- 108090000854 Oxidoreductases Proteins 0.000 description 1
- WTKZEGDFNFYCGP-UHFFFAOYSA-N Pyrazole Chemical compound C=1C=NNC=1 WTKZEGDFNFYCGP-UHFFFAOYSA-N 0.000 description 1
- 238000010802 RNA extraction kit Methods 0.000 description 1
- CGNLCCVKSWNSDG-UHFFFAOYSA-N SYBR Green I Chemical compound CN(C)CCCN(CCC)C1=CC(C=C2N(C3=CC=CC=C3S2)C)=C2C=CC=CC2=[N+]1C1=CC=CC=C1 CGNLCCVKSWNSDG-UHFFFAOYSA-N 0.000 description 1
- 240000006394 Sorghum bicolor Species 0.000 description 1
- 235000011684 Sorghum saccharatum Nutrition 0.000 description 1
- 229910000831 Steel Inorganic materials 0.000 description 1
- 241001464837 Viridiplantae Species 0.000 description 1
- 230000005791 algae growth Effects 0.000 description 1
- 229910000147 aluminium phosphate Inorganic materials 0.000 description 1
- 235000009582 asparagine Nutrition 0.000 description 1
- 229960001230 asparagine Drugs 0.000 description 1
- 235000003704 aspartic acid Nutrition 0.000 description 1
- 230000008901 benefit Effects 0.000 description 1
- OQFSQFPPLPISGP-UHFFFAOYSA-N beta-carboxyaspartic acid Natural products OC(=O)C(N)C(C(O)=O)C(O)=O OQFSQFPPLPISGP-UHFFFAOYSA-N 0.000 description 1
- 108010004337 beta-cyanoalanine synthase Proteins 0.000 description 1
- 230000008512 biological response Effects 0.000 description 1
- 239000007853 buffer solution Substances 0.000 description 1
- 238000005119 centrifugation Methods 0.000 description 1
- 239000003795 chemical substances by application Substances 0.000 description 1
- VDQQXEISLMTGAB-UHFFFAOYSA-N chloramine T Chemical compound [Na+].CC1=CC=C(S(=O)(=O)[N-]Cl)C=C1 VDQQXEISLMTGAB-UHFFFAOYSA-N 0.000 description 1
- 239000002299 complementary DNA Substances 0.000 description 1
- 238000010276 construction Methods 0.000 description 1
- 238000011109 contamination Methods 0.000 description 1
- 230000003247 decreasing effect Effects 0.000 description 1
- 230000000694 effects Effects 0.000 description 1
- 238000009713 electroplating Methods 0.000 description 1
- 238000013401 experimental design Methods 0.000 description 1
- 238000001914 filtration Methods 0.000 description 1
- 239000011888 foil Substances 0.000 description 1
- PCHJSUWPFVWCPO-UHFFFAOYSA-N gold Chemical compound [Au] PCHJSUWPFVWCPO-UHFFFAOYSA-N 0.000 description 1
- 239000010931 gold Substances 0.000 description 1
- 229910052737 gold Inorganic materials 0.000 description 1
- 239000003673 groundwater Substances 0.000 description 1
- 239000001963 growth medium Substances 0.000 description 1
- 239000003501 hydroponics Substances 0.000 description 1
- 230000006872 improvement Effects 0.000 description 1
- 239000003317 industrial substance Substances 0.000 description 1
- 230000008595 infiltration Effects 0.000 description 1
- 238000001764 infiltration Methods 0.000 description 1
- 230000002401 inhibitory effect Effects 0.000 description 1
- 150000002500 ions Chemical class 0.000 description 1
- 238000002386 leaching Methods 0.000 description 1
- 230000000670 limiting effect Effects 0.000 description 1
- 238000005259 measurement Methods 0.000 description 1
- 239000002609 medium Substances 0.000 description 1
- 230000037323 metabolic rate Effects 0.000 description 1
- 239000002184 metal Substances 0.000 description 1
- 229910052751 metal Inorganic materials 0.000 description 1
- 239000012982 microporous membrane Substances 0.000 description 1
- 239000011259 mixed solution Substances 0.000 description 1
- 239000000203 mixture Substances 0.000 description 1
- 238000012986 modification Methods 0.000 description 1
- 230000004048 modification Effects 0.000 description 1
- 235000016709 nutrition Nutrition 0.000 description 1
- 230000035764 nutrition Effects 0.000 description 1
- 230000037361 pathway Effects 0.000 description 1
- 239000000843 powder Substances 0.000 description 1
- 238000002360 preparation method Methods 0.000 description 1
- 239000000047 product Substances 0.000 description 1
- 238000003753 real-time PCR Methods 0.000 description 1
- 238000005067 remediation Methods 0.000 description 1
- 238000010839 reverse transcription Methods 0.000 description 1
- 239000004576 sand Substances 0.000 description 1
- 230000035945 sensitivity Effects 0.000 description 1
- 239000010959 steel Substances 0.000 description 1
- 239000002352 surface water Substances 0.000 description 1
- 238000009210 therapy by ultrasound Methods 0.000 description 1
- 229960001479 tosylchloramide sodium Drugs 0.000 description 1
- 230000001988 toxicity Effects 0.000 description 1
- 231100000419 toxicity Toxicity 0.000 description 1
- 231100000027 toxicology Toxicity 0.000 description 1
- 229910021642 ultra pure water Inorganic materials 0.000 description 1
- 239000012498 ultrapure water Substances 0.000 description 1
Images
Landscapes
- Cultivation Of Plants (AREA)
Abstract
Description
技术领域technical field
本发明属于植物作物学技术领域,涉及植物β-CAS与ST对KCN代谢的贡献率的估算方法。The invention belongs to the technical field of plant crop science, and relates to a method for estimating the contribution rate of plant β-CAS and ST to KCN metabolism.
背景技术Background technique
简单氰化物(KCN)一直是金矿开采过程中首选的浸出剂。此外,它还是金属精加工和硬化、电镀、钢铁和印刷电路板制造行业不可或缺的工业化学品。据统计,每年超过100,000吨来自采矿业的CN-通过地表径流和渗透输送到集水区出口,污染土壤、地表水和地下水。由于其毒性极强,迫切需要一种成本低且可持续的修复方法来去除或解毒环境中的CN-。Simple cyanide (KCN) has been the leaching agent of choice in gold mining. In addition, it is an indispensable industrial chemical for the metal finishing and hardening, electroplating, steel and printed circuit board manufacturing industries. According to statistics, more than 100,000 tons of CN from the mining industry are transported to the outlet of the catchment area through surface runoff and infiltration each year, contaminating soil, surface water and groundwater. Due to its extreme toxicity, a low-cost and sustainable remediation method to remove or detoxify CN- in the environment is urgently needed.
植物修复是利用绿色植物来转移、容纳或转化污染物的方法,以此降低污染物对环境的伤害性。在过去的二十多年中,多种植物被证明可代谢外源KCN,且在植物组织中只能检测到少量的残留CN-,这主要归功于植物体内β-氰丙氨酸合酶(β-CAS)的贡献。β-CAS可将CN-转化为β-氰丙氨酸,其进一步可转化为天冬酰胺或天冬氨酸。此外有文献报道,拟南芥、高粱和木薯中的硫转移酶(ST)被证实也可以代谢CN-,但具体的代谢路径还存有争议。Phytoremediation is the use of green plants to transfer, contain or transform pollutants in order to reduce the harm of pollutants to the environment. In the past two decades, various plants have been shown to metabolize exogenous KCN, and only a small amount of residual CN - can be detected in plant tissues, which is mainly attributed to β-cyanoalanine synthase ( β-CAS). β-CAS can convert CN- to β - cyanoalanine, which can further be converted to asparagine or aspartic acid. In addition, it has been reported in the literature that thiotransferase (ST) in Arabidopsis, sorghum and cassava has been confirmed to metabolize CN - , but the specific metabolic pathway is still controversial.
1-氨基-环丙烷-1-羧酸(ACC)被证实参与植物乙烯的合成,ET合成过程中,氨基环丙烷-1-羧酸氧化酶(ACO)将1-氨基-环丙烷-1-羧酸(ACC)转化为ET并同步伴随产生内源CN-,通过添加外源ACC,可促进受外源KCN胁迫的植物β-CAS和ST对外源CN-代谢,视为一种有效的化学调控剂。1-Amino-cyclopropane-1-carboxylic acid (ACC) has been confirmed to be involved in the synthesis of ethylene in plants. During the synthesis of ET, aminocyclopropane-1-carboxylic acid oxidase (ACO) converts 1-amino-cyclopropane-1- Carboxylic acid (ACC) is converted into ET and synchronously produces endogenous CN - . By adding exogenous ACC, it can promote the metabolism of exogenous CN - by β-CAS and ST in plants stressed by exogenous KCN, which is regarded as an efficient chemical regulator.
综合上述,在植物作物学领域,植物体内β-CAS和ST对外源KCN的代谢贡献率尚不清楚,而β-CAS和ST又关乎外源KCN在植物体内的代谢路径和产物,直接关乎植物对KCN修复效率的评估,亟待一种行之有效的植物β-CAS与ST对KCN代谢的贡献率的估算方法。Based on the above, in the field of plant crops, the contribution rate of β-CAS and ST to exogenous KCN metabolism in plants is not clear, and β-CAS and ST are related to the metabolic pathways and products of exogenous KCN in plants, and are directly related to plants. For the evaluation of KCN repair efficiency, an effective method for estimating the contribution rate of plant β-CAS and ST to KCN metabolism is urgently needed.
发明内容SUMMARY OF THE INVENTION
为了达到上述目的,本发明提供植物β-CAS与ST对KCN代谢的贡献率的估算方法,将植物幼苗水培反应体系等效为植物水培全混生物反应器,通过植物水培全混生物反应器营养液中KCN的浓度与胁迫时间的拟合得到植物水培全混生物反应器中的KCN代谢速率曲线,继而模拟不同时间植物水培全混合反应器对KCN的代谢量,避免了植物修复评价过程中繁琐的时间动力学实验,并且通过与无添加ACC的KCN处理组进行比对,从而形成“边界条件”评价植物β-CAS与ST对外源KCN代谢的贡献率,有利于评估植物对KCN修复效率,解决了现有技术中存在的缺乏植物内源酶对外源胁迫物代谢贡献率的估算方法的问题。In order to achieve the above purpose, the present invention provides a method for estimating the contribution rate of plant β-CAS and ST to KCN metabolism. The plant seedling hydroponic reaction system is equivalent to a plant hydroponic total hybrid bioreactor. The KCN metabolism rate curve in the plant hydroponic total mixed bioreactor was obtained by fitting the concentration of KCN in the nutrient solution of the reactor and the stress time, and then the metabolism of KCN in the plant hydroponic total mixed reactor at different times was simulated to avoid plant hydroponic total mixing. The tedious time kinetic experiments in the repair evaluation process, and the comparison with the KCN treatment group without ACC, thus forming a "boundary condition" to evaluate the contribution rate of plant β-CAS and ST to exogenous KCN metabolism, which is conducive to evaluating plants For the KCN repair efficiency, the problem of lack of estimation methods for the contribution rate of plant endogenous enzymes to metabolism of exogenous stress substances in the prior art is solved.
本发明所采用的技术方案是,植物β-CAS与ST对KCN代谢的贡献率的估算方法,包括以下步骤:The technical solution adopted in the present invention is that the method for estimating the contribution rate of plant β-CAS and ST to KCN metabolism includes the following steps:
步骤1:在多个营养液中分别置入相同数量的植物幼苗,形成多个处理组;一部分处理组营养液中加入不同含量的KCN,构成多个KCN处理组;另一部分处理组营养液中先加入一定质量的ACC,再加入不同含量的KCN,构成多个KCN+ACC处理组;每个处理组中KCN对植物幼苗进行2天短期胁迫;Step 1: Put the same number of plant seedlings into multiple nutrient solutions respectively to form multiple treatment groups; a part of the nutrient solutions of the treatment groups are added with different contents of KCN to form multiple KCN treatment groups; the other part of the nutrient solutions of the treatment groups are A certain quality of ACC was added first, and then different contents of KCN were added to form multiple KCN+ACC treatment groups; KCN in each treatment group was subjected to short-term stress on plant seedlings for 2 days;
步骤2:测定每个处理组短期胁迫前后营养液的KCN含量,以及短期胁迫后植物幼苗体内的CN-含量以及SCN-含量;测定每个处理组短期胁迫后的植物幼苗体内调控β-CAS和ST的相关基因的差异表达水平;Step 2: Determine the KCN content of the nutrient solution before and after short-term stress in each treatment group, and the CN - content and SCN - content in plant seedlings after short-term stress; determine the regulation of β-CAS and SCN-content in plant seedlings after short-term stress in each treatment group. Differential expression levels of ST-related genes;
步骤3:根据每个处理组短期胁迫前后营养液的KCN含量、短期胁迫后植物幼苗体内的CN-含量得到每个处理组植物幼苗对KCN的代谢量;根据每个处理组植物幼苗对KCN的代谢量,得到每个处理组植物幼苗对KCN代谢的速率;Step 3: According to the KCN content of the nutrient solution before and after the short-term stress in each treatment group, and the CN - content in the plant seedlings after the short-term stress, the metabolic amount of KCN in the plant seedlings of each treatment group was obtained; Metabolic amount, the rate of KCN metabolism by plant seedlings in each treatment group was obtained;
步骤4:每个处理组的植物幼苗水培反应体系等效为植物水培全混生物反应器,根据每个处理组营养液中KCN的浓度、植物幼苗的蒸腾量、KCN在植物水培全混生物反应器中的衰减速率常数、植物水培全混生物反应器的体积,构建不包含空间变量的植物水培全混生物反应器对KCN代谢的微分方程;Step 4: The hydroponic reaction system of plant seedlings in each treatment group is equivalent to a plant hydroponic total mixed bioreactor. The decay rate constant in the mixed bioreactor, the volume of the plant hydroponic total mixed bioreactor, and the differential equation of KCN metabolism in the plant hydroponic total mixed bioreactor without spatial variables;
步骤5:根据各处理组植物水培全混生物反应器对KCN代谢的微分方程,得到各处理组营养液中KCN浓度与时间的关系,再根据质量换算得到各处理组植物水培全混生物反应器对KCN的代谢量与时间的关系;根据各KCN处理组和各KCN+ACC处理组植物水培全混生物反应器对KCN的代谢量与时间的关系,得到估算植物β-CAS与ST对KCN代谢的贡献率的物质平衡方程;Step 5: According to the differential equation of KCN metabolism in the plant hydroponic total mixed bioreactor of each treatment group, the relationship between the concentration of KCN in the nutrient solution of each treatment group and time is obtained, and then according to the mass conversion, the plant hydroponic total mixed organism of each treatment group is obtained The relationship between the amount of KCN metabolism in the reactor and time; according to the relationship between the amount of KCN metabolism in the hydroponic total mixed bioreactor of each KCN treatment group and each KCN+ACC treatment group, the estimated plant β-CAS and ST were obtained. The mass balance equation of the contribution rate to KCN metabolism;
步骤6:每个处理组植物幼苗对KCN的代谢量由β-CAS对KCN的代谢量与ST对KCN的代谢量组成;每个处理组植物幼苗ST对KCN的代谢量根据植物幼苗体内产生的SCN-总量得到;植物幼苗体内产生的SCN-总量由植物幼苗体内的SCN-累计量与植物幼苗对SCN-的代谢量构成;每个处理组植物幼苗体内的SCN-累计量为步骤2测定的短期胁迫后植物幼苗体内的SCN-含量;Step 6: The amount of metabolism of KCN by plant seedlings in each treatment group is composed of the amount of metabolism of β-CAS to KCN and the amount of metabolism of ST to KCN; the amount of metabolism of plant seedlings of ST to KCN in each treatment group is based on the amount of The total amount of SCN- is obtained; the total amount of SCN- produced in plant seedlings is composed of the cumulative amount of SCN- in plant seedlings and the amount of SCN- metabolized in plant seedlings; the cumulative amount of SCN- in plant seedlings of each treatment group is
以0.5μg为步长单位设置各KCN处理组植物幼苗对SCN-的代谢量的数值,以植物幼苗体内的SCN-累计量为中间条件,当计算到各KCN处理组中β-CAS或ST对KCN的代谢量为最大值停止计算;The value of SCN - metabolism in plant seedlings of each KCN treatment group was set with 0.5 μg as a step unit, and the cumulative amount of SCN - in plant seedlings was used as an intermediate condition. When calculating the amount of β-CAS or ST in each KCN treatment group The metabolic amount of KCN is calculated at the maximum value;
以0.5μg为步长单位设置各KCN+ACC处理组植物幼苗对SCN-的代谢量的数值,以植物幼苗体内的SCN-累计量为中间条件,当计算到各KCN+ACC处理组中β-CAS或ST对KCN的代谢量为最大值停止计算;The value of SCN - metabolism in plant seedlings in each KCN+ACC treatment group was set with 0.5 μg as a step unit, and the cumulative amount of SCN - in plant seedlings was used as the intermediate condition. The metabolism of CAS or ST to KCN is the maximum value and the calculation is stopped;
根据KCN+ACC处理组中β-CAS或ST对KCN的代谢量总是大于KCN处理组中β-CAS或ST对KCN的代谢量,得到植物β-CAS与ST对KCN代谢的贡献率的范围,完成植物β-CAS与ST对KCN代谢的贡献率的估算。According to the metabolism of β-CAS or ST to KCN in the KCN+ACC treatment group is always greater than the metabolism of β-CAS or ST to KCN in the KCN treatment group, the range of the contribution rate of plant β-CAS and ST to KCN metabolism was obtained. , to complete the estimation of the contribution rate of plant β-CAS and ST to KCN metabolism.
进一步地,步骤2还包括,根据测定的每个处理组短期胁迫后的植物幼苗体内调控β-CAS和ST的相关基因的差异表达水平,得到同一胁迫浓度下KCN+ACC处理组植物幼苗体内调控β-CAS和ST的相关基因的差异表达水平高于KCN处理组。Further,
进一步地,步骤3中,每个处理组植物幼苗对KCN代谢的速率为短期胁迫时间内每个处理组对KCN的代谢量与每个处理组植物幼苗鲜重的比值。Further, in
进一步地,步骤4中,不包含空间变量的植物水培全混生物反应器对KCN代谢的浓度微分方程,如下式所示:Further, in
式中,C(t)表示t时营养液中KCN的浓度,单位是μg/mL;β表示修正系数;Q表示植物幼苗的蒸腾量,单位是g/h;Ci表示营养液中KCN的起始浓度,单位是μg/mL;k表示KCN在植物水培全混生物反应器中的衰减速率常数,单位是h-1;V表示植物水培全混生物反应器的体积,单位是mL;t表示时间,单位是h;e是自然常数。In the formula, C (t) represents the concentration of KCN in the nutrient solution at t, in μg/mL; β represents the correction coefficient; Q represents the transpiration of plant seedlings, in g/h; C i represents the concentration of KCN in the nutrient solution. Initial concentration, the unit is μg/mL; k is the decay rate constant of KCN in the plant hydroponic total mixed bioreactor, the unit is h -1 ; V is the volume of the plant hydroponic total mixed bioreactor, the unit is mL ; t represents time in h; e is a natural constant.
更进一步地,修正系数的计算,如下式所示:Further, the calculation of the correction coefficient is as follows:
更进一步地,KCN在植物水培全混生物反应器中的衰减速率常数的获得,具体为:以各KCN处理组或各KCN+ACC处理组营养液中KCN的起始浓度为自变量,对各KCN处理组或各KCN+ACC处理组植物幼苗对KCN代谢的速率进行线性拟合,拟合曲线的斜率即为KCN处理组或KCN+ACC处理组中KCN在植物水培全混生物反应器中的衰减速率常数。Further, the acquisition of the decay rate constant of KCN in the plant hydroponic total mixed bioreactor is specifically: taking the initial concentration of KCN in the nutrient solution of each KCN treatment group or each KCN+ACC treatment group as an independent variable, The rate of KCN metabolism in each KCN treatment group or each KCN+ACC treatment group was linearly fitted, and the slope of the fitting curve was the KCN in the KCN treatment group or the KCN+ACC treatment group in the plant hydroponic total mixed bioreactor. The decay rate constant in .
更进一步地,植物幼苗的蒸腾量即为单位胁迫时间植物水培全混生物反应器总重量的变化量。Furthermore, the transpiration of plant seedlings is the change in the total weight of the plant hydroponic total mixed bioreactor per unit stress time.
进一步地,步骤6中,每个处理组植物幼苗ST对KCN的代谢量根据植物幼苗体内产生的SCN-总量得到,具体为:植物幼苗体内产生的SCN-总量与植物幼苗ST对KCN的代谢量的化学计量比为1:1,由植物幼苗体内产生的SCN-总量的摩尔量得到植物幼苗ST对KCN的代谢量的摩尔量,经质量换算,得到每个处理组植物幼苗ST对KCN的代谢量。Further, in
进一步地,步骤6中,β-CAS与ST对KCN代谢的贡献率,具体为:β-CAS或ST对KCN的代谢量占植物幼苗对KCN的代谢量的质量百分比。Further, in
本发明的有益效果是:本发明实施例选择ACC为化学调控剂,运用植物毒理学手段,对植物幼苗进行KCN短期胁迫;将植物幼苗水培反应体系等效为植物水培全混生物反应器,通过植物水培全混生物反应器营养液中KCN的浓度与胁迫时间的拟合得到植物水培全混生物反应器中的KCN代谢速率曲线,继而模拟不同时间植物水培全混合反应器对KCN的代谢量,避免了植物修复评价过程中繁琐的时间动力学实验,并且通过与无添加ACC的KCN处理组进行比对,从而形成“边界条件”评价植物β-CAS与ST对外源KCN代谢的贡献率,本发明实施例植物β-CAS与ST对KCN代谢的贡献率的估算方法有利于后续评估植物对KCN修复效率。The beneficial effects of the present invention are: in the embodiment of the present invention, ACC is selected as a chemical regulator, and plant toxicology methods are used to carry out short-term KCN stress on plant seedlings; the hydroponic reaction system of plant seedlings is equivalent to a plant hydroponic total mixed bioreactor , the KCN metabolism rate curve in the plant hydroponic total mixed bioreactor was obtained by fitting the concentration of KCN in the nutrient solution of the plant hydroponic total mixed bioreactor and the stress time, and then simulated the plant hydroponic total mixed reactor at different times. The metabolism of KCN avoids the tedious time kinetic experiments in the phytoremediation evaluation process, and is compared with the KCN treatment group without ACC to form a "boundary condition" to evaluate the metabolism of plant β-CAS and ST to exogenous KCN The method for estimating the contribution rate of plant β-CAS and ST to KCN metabolism in the embodiment of the present invention is beneficial to the subsequent evaluation of plant restoration efficiency of KCN.
附图说明Description of drawings
为了更清楚地说明本发明实施例或现有技术中的技术方案,下面将对实施例或现有技术描述中所需要使用的附图作简单地介绍,显而易见地,下面描述中的附图仅仅是本发明的一些实施例,对于本领域普通技术人员来讲,在不付出创造性劳动的前提下,还可以根据这些附图获得其他的附图。In order to explain the embodiments of the present invention or the technical solutions in the prior art more clearly, the following briefly introduces the accompanying drawings that need to be used in the description of the embodiments or the prior art. Obviously, the accompanying drawings in the following description are only These are some embodiments of the present invention. For those of ordinary skill in the art, other drawings can also be obtained according to these drawings without creative efforts.
图1是本发明实施例植物β-CAS与ST对KCN代谢的贡献率的估算方法的流程图。Fig. 1 is a flow chart of the method for estimating the contribution rate of plant β-CAS and ST to KCN metabolism according to the embodiment of the present invention.
图2是本发明实施例各处理组水稻幼苗体内的CN-含量结果,图2中a为各KCN处理组水稻幼苗体内的CN-含量,图2中b为各ACC+KCN处理组水稻幼苗体内的CN-含量。Fig. 2 is the result of CN -content in the rice seedlings of each treatment group according to the embodiment of the present invention, in Fig. 2 a is the CN- content in the rice seedlings of each KCN treatment group, and b in Fig. 2 is the in vivo content of the rice seedlings of each ACC+KCN treatment group CN - content.
图3是本发明实施例各处理组水稻幼苗体内的SCN-含量结果,图3中a为各KCN处理组水稻幼苗体内SCN-的含量,图3中b为各ACC+KCN处理组水稻幼苗体内SCN-的含量。Fig. 3 is the result of SCN - content in rice seedlings of each treatment group according to the embodiment of the present invention, in Fig. 3 a is the content of SCN - in rice seedlings of each KCN treatment group, and b in Fig. 3 is the in vivo content of rice seedlings of each ACC+KCN treatment group SCN - content.
图4a是本发明实施例各KCN处理组β-CAS和ST候选基因差异表达水平的分析图。Figure 4a is an analysis diagram of the differential expression levels of β-CAS and ST candidate genes in each KCN treatment group according to the embodiment of the present invention.
图4b是本发明实施例各ACC+KCN处理组β-CAS和ST候选基因差异表达水平的分析图。Figure 4b is an analysis diagram of the differential expression levels of β-CAS and ST candidate genes in each ACC+KCN treatment group according to the embodiment of the present invention.
图5是本发明实施例水稻水培全混生物反应器模型示意图。Fig. 5 is a schematic diagram of a model of a rice hydroponic total mixed bioreactor according to an embodiment of the present invention.
图6是本发明实施例KCN在水稻水培全混生物反应器中的衰减速率常数图,图6中a是各KCN处理组KCN在水稻水培全混生物反应器中的衰减速率常数图,图6中b是各ACC+KCN处理组KCN在水稻水培全混生物反应器中的衰减速率常数图。Fig. 6 is the decay rate constant diagram of KCN in the rice hydroponic total mixed bioreactor according to the embodiment of the present invention, in Fig. 6 a is the decay rate constant diagram of KCN in each KCN treatment group in the rice hydroponic total mixed bioreactor, In Figure 6, b is the decay rate constant diagram of KCN in each ACC+KCN treatment group in the rice hydroponic total mixed bioreactor.
图7是本发明实施例KCN在水稻水培全混生物反应器中代谢的时间动力学特征图。FIG. 7 is a time kinetic characteristic diagram of KCN metabolism in a rice hydroponic total mixed bioreactor according to an embodiment of the present invention.
具体实施方式Detailed ways
下面将结合本发明实施例中的附图,对本发明实施例中的技术方案进行清楚、完整地描述,显然,所描述的实施例仅仅是本发明一部分实施例,而不是全部的实施例。基于本发明中的实施例,本领域普通技术人员在没有做出创造性劳动前提下所获得的所有其他实施例,都属于本发明保护的范围。The technical solutions in the embodiments of the present invention will be clearly and completely described below with reference to the accompanying drawings in the embodiments of the present invention. Obviously, the described embodiments are only a part of the embodiments of the present invention, rather than all the embodiments. Based on the embodiments of the present invention, all other embodiments obtained by those of ordinary skill in the art without creative efforts shall fall within the protection scope of the present invention.
植物β-CAS与ST对KCN代谢的贡献率的估算方法,如图1所示,包括以下步骤:The method for estimating the contribution rate of plant β-CAS and ST to KCN metabolism, as shown in Figure 1, includes the following steps:
1、水稻幼苗的准备1. Preparation of rice seedlings
水稻种子在水中浸泡12小时,然后种子放入一次性纸杯中进行沙土培养,种植密度为:约水稻30-40颗/杯。培养在人工气候箱中进行,温度为25℃,湿度为65%,光照强度20000lux。使用改良版的ISO8692营养液浇灌水稻,如表1所示,水稻生长16天后,将其根部的沙土清洗干净,选取个体大小均与一致的水稻幼苗备用。The rice seeds are soaked in water for 12 hours, and then the seeds are put into disposable paper cups for sand cultivation. The planting density is about 30-40 rice per cup. Cultivation was carried out in an artificial climate box at a temperature of 25° C., a humidity of 65%, and a light intensity of 20,000 lux. The rice was irrigated with an improved version of ISO8692 nutrient solution, as shown in Table 1. After the rice was grown for 16 days, the sandy soil at its roots was cleaned, and rice seedlings with the same individual size were selected for use.
表1改良版的ISO8692营养液Table 1 Improved version of ISO8692 nutrient solution
2、实验设计2. Experimental design
选定的水稻幼苗在以下处理溶液中培养:Selected rice seedlings were grown in the following treatment solutions:
KCN处理组:将四组水稻幼苗,鲜重分别为1.291g、1.285g、1.244g和1.223g,分别放置于50mL锥形瓶中,并加入了50mL如表1所示的改良版的ISO8692营养液,并分别添加0mg/L、1.0mg/L、2.0mg/L、3.0mg/L的KCN。KCN treatment group: Four groups of rice seedlings with fresh weights of 1.291g, 1.285g, 1.244g and 1.223g were placed in 50mL conical flasks, and 50mL of the improved version of ISO8692 nutrition as shown in Table 1 was added. solution, and added 0 mg/L, 1.0 mg/L, 2.0 mg/L, and 3.0 mg/L of KCN, respectively.
KCN+ACC处理组:将四组水稻幼苗,鲜重分别为1.293g、1.29g、1.263g、1.244g,分别放置于50mL锥形瓶中,并加入了50mL如表1所示的改良版的ISO8692营养液,并分别添加10μM的ACC,然后再分别添加0mg/L、1.0mg/L、2.0mg/L、3.0mg/L的KCN。KCN+ACC treatment group: Four groups of rice seedlings with fresh weights of 1.293g, 1.29g, 1.263g, and 1.244g were placed in 50mL conical flasks, and 50mL of the improved version shown in Table 1 was added. ISO8692 nutrient solution was added with 10 μM ACC, and then 0 mg/L, 1.0 mg/L, 2.0 mg/L and 3.0 mg/L KCN were added respectively.
每个锥形瓶都用锡箔纸包裹做避光处理,最大限度地减少水分流失并抑制藻类生长。每个处理组均有4个生物学重复,短期暴露时间为2天。本实验所用试剂均为分析纯。Each Erlenmeyer flask is wrapped in foil to protect from light, minimizing water loss and inhibiting algae growth. Each treatment group had 4 biological replicates with a short-term exposure of 2 days. All reagents used in this experiment were of analytical grade.
2.1、营养液中KCN含量和水稻幼苗体内总CN-含量的分析2.1. Analysis of KCN content in nutrient solution and total CN - content in rice seedlings
2.1.1、营养液中KCN含量测定2.1.1. Determination of KCN content in nutrient solution
分别在暴露前和暴露结束后(2天)测定营养液中KCN的浓度。用比色管中收集一定体积的溶液样品(1mL~5mL),并加入NaOH(0.1%)至10mL刻度线。然后,加入含有KH2PO4和NaH2PO4的缓冲溶液(5.0mL),迅速加入氯胺-T溶液(0.2mL,1%[m/v]),摇匀放置3min~5min,再加入异烟酸和吡唑啉酮混合液,用MilliQ水(超纯水)定容至25mL,混匀,将比色管置于水浴中(32℃,40分钟),最后,在638nm处用分光光度计测定营养液中的KCN含量。The concentration of KCN in the nutrient solution was measured before and after exposure (2 days), respectively. A certain volume of solution sample (1 mL-5 mL) was collected in a colorimetric tube, and NaOH (0.1%) was added to the 10 mL mark. Then, a buffer solution (5.0 mL) containing KH 2 PO 4 and NaH 2 PO 4 was added, and chloramine-T solution (0.2 mL, 1% [m/v]) was added quickly, shaken for 3 min to 5 min, and then added The mixture of isonicotinic acid and pyrazolone is made up to 25mL with MilliQ water (ultrapure water), mixed well, and the colorimetric tube is placed in a water bath (32°C, 40 minutes). The KCN content in the nutrient solution was determined by a photometer.
其中,异烟酸和吡唑啉酮混合液5.0mL,由异烟酸(1.5g异烟酸溶于24mL 2%的NaOH溶液中,加水稀释到100mL)∶吡唑啉酮(0.25g吡唑啉酮溶于20mL二甲基甲酰胺溶液中)配制而成。Among them, 5.0 mL of isonicotinic acid and pyrazolone mixed solution is composed of isonicotinic acid (1.5 g of isonicotinic acid is dissolved in 24 mL of 2% NaOH solution, diluted with water to 100 mL): pyrazolone (0.25 g of pyrazole citronone dissolved in 20 mL of dimethylformamide solution).
2.1.2水稻幼苗体内总CN-含量检测2.1.2 Detection of total CN - content in rice seedlings
用蒸馏法测定水稻幼苗体内总CN-含量。将10mL的NaOH(1%)溶液加入到蒸馏系统的末端的收集瓶中。将准确称重的切碎的水稻幼苗根或叶片样品放入圆底烧瓶(500mL)中,加入200mL的MilliQ水,然后加入10mL的EDTA(10%)溶液和10mL的磷酸(85%),启动蒸馏系统,当收集瓶中的溶液接近100mL时,关闭蒸馏系统,并将收集瓶中的液体转移到容量瓶(100mL)定容待测,收集液中CN-的含量测定分析参照2.1.1,测试结果如图2所示。Determination of total CN - content in rice seedlings by distillation. 10 mL of NaOH (1%) solution was added to the collection flask at the end of the distillation system. Place an accurately weighed sample of chopped rice seedling roots or leaves into a round bottom flask (500 mL), add 200 mL of MilliQ water, then 10 mL of EDTA (10%) solution and 10 mL of phosphoric acid (85%), start Distillation system, when the solution in the collection bottle is close to 100mL , close the distillation system, and transfer the liquid in the collection bottle to a volumetric flask (100mL) to constant volume to be measured. The test results are shown in Figure 2.
2.2、水稻幼苗体内SCN-含量的检测2.2. Detection of SCN - content in rice seedlings
水稻幼苗在2天暴露后,分别收集水稻幼苗的根和叶片并称重,并立即在液氮中研磨成粉状,随后,将粉状样品与5mL的柠檬酸(0.1M)混合,在25℃,40kHz超声处理1h,10,000×g低温(4℃)离心10min,收集上清液。此过程重复2次,并将2次的上清液混合。最后,使用旋转蒸发器浓缩样品(~2.0mL)。用0.45μm微孔滤膜过滤后,用离子色谱仪测定SCN-含量,测试结果如图3所示。After 2-day exposure of rice seedlings, the roots and leaves of rice seedlings were collected and weighed, and immediately ground into powder in liquid nitrogen. Subsequently, the powdered samples were mixed with 5 mL of citric acid (0.1 M) at 25 ℃, 40kHz ultrasonic treatment for 1h, 10,000×g low temperature (4℃) centrifugation for 10min, and the supernatant was collected. This process was repeated 2 times, and the supernatants of the 2 times were mixed. Finally, the sample (~2.0 mL) was concentrated using a rotary evaporator. After filtration with a 0.45 μm microporous membrane, the SCN - content was measured by an ion chromatograph. The test results are shown in Figure 3.
2.3、β-CAS和ST相关基因差异表达的分析2.3. Analysis of differential expression of β-CAS and ST-related genes
本发明采用3个调控β-CAS的基因(OsCYS-C1、OsCYS-D1和OsCYS-D2)。据报道,拟南芥ST家族基因中的AtStr1和AtStr2明确参与CN-代谢,因此从水稻数据库RGAP(http://rice.plantbiology.msu.edu/analyses_search_blast.shtm),国家水稻数据中心(http://www.ricedata.cn/gene/index.htm),和RAP-DB(http://rapdb.dna.affrc.go.jp/)中筛选出与拟南芥中参与CN-代谢同源性较高的3个基因(OsStr9、OsStr23和OsStr24)。The present invention adopts three genes (OsCYS-C1, OsCYS-D1 and OsCYS-D2) that regulate β-CAS. It has been reported that AtStr1 and AtStr2 in Arabidopsis ST family genes are explicitly involved in CN - metabolism, thus obtained from the Rice Database RGAP (http://rice.plantbiology.msu.edu/analyses_search_blast.shtm), National Rice Data Center (http: //www.ricedata.cn/gene/index.htm), and RAP-DB (http://rapdb.dna.affrc.go.jp/) screened out the homology with Arabidopsis involved in CN - metabolism The higher 3 genes (OsStr9, OsStr23 and OsStr24).
实时定量PCR(qRT-PCR)用于测定β-CAS和ST的基因差异表达水平,如表2所示。2天暴露处理后,称取0.2g水稻幼苗组织并立即在液氮中研磨,使用RNA提取试剂盒提取样品的总RNA,采用超微分光光度计检测提取RNA的A260/A280在1.8-2.0之间,用DNase I去除gDNA的污染,然后采用反转录试剂盒进行cDNA的第一链合成,采用SYBR green I染料法进行实时荧光定量PCR(qRT-PCR);选定的6个候选基因用Primer5.0设计引物,使用AB-7500型定量PCR仪分析基因的表达,差异表达倍数采用2-ΔΔCT计算,测定结果如图4a和图4b所示。Quantitative real-time PCR (qRT-PCR) was used to determine the gene differential expression levels of β-CAS and ST, as shown in Table 2. After 2 days of exposure treatment, 0.2 g of rice seedling tissue was weighed and immediately ground in liquid nitrogen, the total RNA of the sample was extracted using an RNA extraction kit, and the A260/A280 of the extracted RNA was detected by an ultra-microspectrophotometer between 1.8 and 2.0. DNase I was used to remove the contamination of gDNA, then reverse transcription kit was used to synthesize the first strand of cDNA, and SYBR green I dye method was used to perform real-time quantitative PCR (qRT-PCR). Primer 5.0 was used to design primers, and AB-7500 quantitative PCR instrument was used to analyze gene expression. The differential expression fold was calculated by 2 -ΔΔCT . The measurement results are shown in Figure 4a and Figure 4b.
表2水稻幼苗β-CAS和ST候选基因的引物设计Table 2 Primer design of β-CAS and ST candidate genes in rice seedlings
3、实验结果3. Experimental results
3.1、营养液中KCN含量与水稻幼苗体内CN-含量的分析3.1. Analysis of KCN content in nutrient solution and CN- content in rice seedlings
反应起始,加入到50mL反应器营养液中KCN浓度分别为1.0mg/L、2.0mg/L、3.0mg/L,因此,计算得出添加的外源KCN分别为50μg、100μg和150μg;2天暴露结束后,测定营养液中KCN浓度,并根据公式(1)计算营养液中KCN的去除率R,具体计算结果如表3所示:At the beginning of the reaction, the concentrations of KCN added to the nutrient solution of the 50 mL reactor were 1.0 mg/L, 2.0 mg/L, and 3.0 mg/L, respectively. Therefore, the calculated exogenous KCN added was 50 μg, 100 μg, and 150 μg, respectively; 2 After the end of day exposure, measure the KCN concentration in the nutrient solution, and calculate the removal rate R of KCN in the nutrient solution according to formula (1), and the specific calculation results are shown in Table 3:
式中,Cf表示胁迫结束营养液中KCN浓度,Vf表示胁迫结束营养液的体积,Ci表示胁迫前营养液中KCN浓度,Vi表示胁迫前营养液的体积。In the formula, C f represents the KCN concentration in the nutrient solution at the end of the stress, V f represents the volume of the nutrient solution at the end of the stress, Ci represents the KCN concentration in the nutrient solution before the stress, and Vi represents the volume of the nutrient solution before the stress.
表3营养液中KCN的去除率Table 3 Removal rate of KCN in nutrient solution
从表3可得到结论:KCN+ACC处理组的KCN去除率要高于KCN处理组。It can be concluded from Table 3 that the KCN removal rate of the KCN+ACC treatment group was higher than that of the KCN treatment group.
3.2、各处理组水稻幼苗体内CN-的含量结果分析3.2. Analysis of CN - content in rice seedlings in each treatment group
从图2中可以看出,随着营养液KCN含量的增加,水稻幼苗根和叶片中的CN-浓度显著增加。如图2中a所示,KCN处理组根和叶片中CN-的浓度分别在0.64μg/g~1.58μg/g和0.38μg/g~1.14μg/g之间。如图2中b所示,在KCN+ACC处理组,根和叶片中CN-的水平分别介于0.28μg/g~0.36μg/g和0.23μg/g~0.31μg/g之间。显然,KCN+ACC处理组的水稻幼苗根和叶片中残留的CN-浓度显著低于KCN处理组,表明在外源KCN短期胁迫下,外源添加ACC可以减少水稻幼苗中CN-的残留。As can be seen from Figure 2, with the increase of KCN content in the nutrient solution, the CN - concentration in the roots and leaves of rice seedlings increased significantly. As shown in a in Fig. 2, the concentrations of CN - in the roots and leaves of the KCN-treated groups were between 0.64 μg/g and 1.58 μg/g and 0.38 μg/g and 1.14 μg/g, respectively. As shown in b in Fig. 2, in the KCN+ACC treatment group, the levels of CN − in roots and leaves ranged from 0.28 μg/g to 0.36 μg/g and 0.23 μg/g to 0.31 μg/g, respectively. Obviously, the residual CN - concentrations in the roots and leaves of rice seedlings in the KCN+ACC treatment group were significantly lower than those in the KCN treatment group, indicating that exogenous addition of ACC could reduce the residual CN - in rice seedlings under short-term exogenous KCN stress.
3.3、水稻幼苗对KCN代谢的速率计算3.3. Rate calculation of KCN metabolism by rice seedlings
根据KCN在水稻水培全混生物反应器中物质平衡得知,水稻幼苗对KCN的代谢量=水稻幼苗对KCN的吸收量-水稻幼苗体内CN-的累积量。因此,可计算得到48h时水稻幼苗对KCN代谢的速率,如表4所示。According to the material balance of KCN in the rice hydroponic total mixed bioreactor, the metabolism of KCN by rice seedlings = the absorption of KCN by rice seedlings - the accumulation of CN - in rice seedlings. Therefore, the rate of KCN metabolism by rice seedlings at 48h can be calculated, as shown in Table 4.
表4 48h水稻幼苗对KCN代谢的速率Table 4 Metabolism rate of KCN by 48h rice seedlings
表4中,48h水稻幼苗对KCN的单位是μg/g FW·h,FW表示水稻幼苗鲜重(g)。从表4可知,外源添加ACC能有效提高水稻幼苗对KCN的代谢速率。In Table 4, the effect of 48h rice seedlings on KCN The unit is μg/g FW·h, and FW represents the fresh weight of rice seedlings (g). It can be seen from Table 4 that exogenous addition of ACC can effectively increase the metabolic rate of KCN in rice seedlings.
3.4、水稻幼苗体内SCN-含量的分析3.4. Analysis of SCN - content in rice seedlings
从图3可知,随着KCN添加量的增加,水稻幼苗根和叶片中SCN-的浓度显著增加。如图3中a所示,KCN处理组中根和叶片中SCN-的浓度范围分别在12.21μg/g~37.69μg/g和8.71μg/g~26.69μg/g之间。如图3中b所示,KCN+ACC处理组中根和叶片中SCN-的浓度分别介于8.65μg/g~25.87μg/g和5.98μg/g~19.23μg/g之间。显然,KCN+ACC处理组水稻幼苗根和叶片中SCN-浓度显著低于KCN处理组,表明添加外源ACC能降低KCN胁迫下水稻幼苗组织中SCN-的积累。It can be seen from Fig. 3 that with the increase of KCN addition, the concentration of SCN - in the roots and leaves of rice seedlings increased significantly. As shown in a in Fig. 3, the concentrations of SCN- in roots and leaves in the KCN-treated group ranged from 12.21 μg/g to 37.69 μg/g and 8.71 μg/g to 26.69 μg/g, respectively. As shown in b in Fig. 3, the concentrations of SCN- in roots and leaves in the KCN+ACC treatment group ranged from 8.65 μg/g to 25.87 μg/g and 5.98 μg/g to 19.23 μg/g, respectively. Obviously, the SCN - concentration in the roots and leaves of rice seedlings in the KCN+ACC treatment group was significantly lower than that in the KCN treatment group, indicating that the addition of exogenous ACC could reduce the accumulation of SCN - in the tissues of rice seedlings under KCN stress.
3.5、ST和β-CAS候选基因表达的分析3.5. Analysis of ST and β-CAS candidate gene expression
如图4a和图4b所示,在KCN处理组和KCN+ACC处理组,水稻幼苗3个ST候选基因的差异表达水平在根和叶片中均上调,其中KCN+ACC处理组3个候选ST基因的差异表达水平均显着高于KCN处理组。与ST基因的差异表达相似,在KCN处理组和KCN+ACC处理组,水稻幼苗3个β-CAS候选基因的差异表达水平在根和叶片中也均上调,其中KCN+ACC处理组中3个β-CAS候选基因的差异表达水平显著高于KCN处理组。这些结果表明,外源添加ACC可以正向提高β-CAS和ST基因在水稻幼苗组织中的差异表达水平。As shown in Figure 4a and Figure 4b, in the KCN treatment group and the KCN+ACC treatment group, the differential expression levels of the three ST candidate genes in rice seedlings were up-regulated in both roots and leaves, among which the three candidate ST genes in the KCN+ACC treatment group were The differential expression levels were significantly higher than those in the KCN-treated group. Similar to the differential expression of ST genes, the differential expression levels of three β-CAS candidate genes in rice seedlings were also up-regulated in roots and leaves in the KCN treatment group and the KCN+ACC treatment group, among which 3 in the KCN+ACC treatment group The differential expression levels of β-CAS candidate genes were significantly higher than those in the KCN-treated group. These results indicated that exogenous addition of ACC could positively increase the differential expression levels of β-CAS and ST genes in rice seedling tissues.
4、水稻水培全混生物反应模型联合边界条件评估β-CAS和ST对KCN代谢的贡献率4. Evaluation of the contribution rate of β-CAS and ST to KCN metabolism using a rice hydroponic total hybrid biological response model combined with boundary conditions
本发明处理是基于水稻水培反应体系,如图5所示,添加到水稻幼苗生长介质中的外源KCN遵循一级动力学吸收特征进入到水稻幼苗体内,其在水稻幼苗体内的代谢过程也遵循同样的反应规律,以此外源KCN进入水稻水培全混生物反应器后在三维空间上达到均匀混合。The treatment of the present invention is based on the rice hydroponic reaction system. As shown in Figure 5, the exogenous KCN added to the growth medium of rice seedlings enters into the rice seedlings following the first-order kinetic absorption characteristics, and its metabolic process in the rice seedlings is also Following the same reaction law, the exogenous KCN can achieve uniform mixing in three-dimensional space after entering the rice hydroponic total mixing bioreactor.
水稻水培全混生物反应器模型假设:Hybrid bioreactor model assumptions for rice hydroponics:
KCN在水稻水培全混生物反应器符合质量守恒定律;KCN conforms to the law of conservation of mass in the rice hydroponic total mixed bioreactor;
KCN在水稻水培全混生物反应器中遵循一级动力学衰减特征;KCN follows first-order kinetic decay characteristics in a rice hydroponic total mixed bioreactor;
水稻幼苗中仅有β-CAS和ST参与代谢KCN,且受关联基因的调控。In rice seedlings, only β-CAS and ST are involved in the metabolism of KCN and are regulated by associated genes.
4.1、模型构建4.1. Model construction
根据物质平衡建立不包含空间变量的微分方程:Set up a differential equation with no spatial variables from the mass balance:
其中,V表示水稻水培全混生物反应器的体积,单位是mL;C表示营养液中KCN的浓度,单位是μg/mL,t表示时间,单位是h;Q表示水稻幼苗的蒸腾量,单位是g/h;Ci表示营养液中KCN的起始浓度,单位是μg/mL;Cf表示胁迫结束时营养液中KCN的浓度,单位是μg/mL;k表示KCN在水稻水培全混生物反应器中的衰减速率常数,单位是h-1。Among them, V is the volume of the rice hydroponic total mixed bioreactor, the unit is mL; C is the concentration of KCN in the nutrient solution, the unit is μg/mL, t is the time, the unit is h; Q is the transpiration of the rice seedling, The unit is g/h; C i is the initial concentration of KCN in the nutrient solution, the unit is μg/mL; C f is the concentration of KCN in the nutrient solution at the end of the stress, the unit is μg/mL; k is the KCN in the rice hydroponic culture Decay rate constant in a fully mixed bioreactor in h -1 .
非稳态衰减时,根据式(1)得出t时水稻水培全混生物反应器营养液中KCN的浓度C(t),如式(3)所示:When the non-steady state decays, According to the formula (1), the concentration C (t) of KCN in the nutrient solution of the rice hydroponic total mixed bioreactor at t is obtained, as shown in the formula (3):
为了让模拟结果和实际结果更加相近,需要引入修正系数对式(3)进行修正,具体如式(4)所示:In order to make the simulation results more similar to the actual results, it is necessary to introduce a correction coefficient to correct equation (3), as shown in equation (4):
其中,β表示修正系数,e是自然常数。Among them, β represents a correction coefficient, and e is a natural constant.
4.2、参数界定4.2, parameter definition
4.2.1、水稻水培全混生物反应器体积的计算4.2.1. Calculation of volume of rice hydroponic total mixed bioreactor
水稻水培全混生物反应器体积V=m/ρ,其中m表示各处理组水稻幼苗的鲜重(g),水稻幼苗的密度ρ=0.72g/mL,各处理组水稻水培全混生物反应器体积的计算结果如表5所示。The volume of the rice hydroponic total hybrid bioreactor V=m/ρ, where m represents the fresh weight (g) of the rice seedlings in each treatment group, the density of the rice seedlings ρ=0.72g/mL, and the rice hydroponic total hybrid organisms in each treatment group The calculated results of the reactor volume are shown in Table 5.
表5水稻水培全混生物反应器体积Table 5 Rice hydroponic total mixed bioreactor volume
4.2.2、水稻幼苗的蒸腾量计算4.2.2. Calculation of transpiration of rice seedlings
水稻幼苗的蒸腾量等效为单位胁迫时间内水稻水培全混生物反应器的总重量变化量,各处理组水稻幼苗的蒸腾量如表6所示。The transpiration of rice seedlings is equivalent to the change in the total weight of the rice hydroponic total mixed bioreactor per unit stress time. The transpiration of rice seedlings in each treatment group is shown in Table 6.
表6水稻幼苗的蒸腾量Table 6 Transpiration of rice seedlings
4.2.3、KCN在水稻水培全混生物反应器中的衰减速率常数4.2.3. Decay rate constant of KCN in rice hydroponic total mixed bioreactor
根据表4,以KCN胁迫浓度为X轴,水稻幼苗对KCN代谢的速率为Y轴,进行线性拟合,斜率即为衰减速率常数(h-1)。拟合得出:KCN处理组KCN在水稻水培全混生物反应器中的衰减速率常数为0.6141h-1,ACC+KCN处理组KCN在水稻水培全混生物反应器中的衰减速率常数为0.7089h-1,如图6所示。According to Table 4, taking the KCN stress concentration as the X-axis and the rate of KCN metabolism by rice seedlings as the Y-axis, a linear fit was performed, and the slope was the decay rate constant (h -1 ). The fitting results show that the decay rate constant of KCN in the rice hydroponic total mixed bioreactor in the KCN treatment group is 0.6141h -1 , and the decay rate constant of KCN in the ACC+KCN treatment group in the rice hydroponic total mixed bioreactor is 0.7089h -1 , as shown in Figure 6.
4.3、结果输出4.3. Result output
将以上结果分别代入公式(4)得到水稻水培全混生物反应器中营养液中KCN的浓度和时间的关系,再根据质量换算得到水稻水培全混生物反应器对KCN的代谢量和时间的关系,如图7所示。可见外源KCN进入水稻幼苗体内12h之后就进入了代谢的平台期。因此,该模型的一个优势就是模拟不同时间水稻水培全混生物反应器对KCN的代谢量,避免了水稻修复评价过程中繁琐的时间动力学实验。Substitute the above results into formula (4) to obtain the relationship between the concentration and time of KCN in the nutrient solution in the rice hydroponic total-mixed bioreactor, and then obtain the metabolic amount and time of KCN in the rice hydroponic total-mixed bioreactor according to the mass conversion. relationship, as shown in Figure 7. It can be seen that the exogenous KCN entered the metabolic plateau 12h after entering the rice seedlings. Therefore, one of the advantages of this model is to simulate the metabolism of KCN in the rice hydroponic total mixed bioreactor at different times, avoiding the tedious time kinetic experiments in the process of rice restoration evaluation.
4.4、水稻幼苗β-CAS和ST对KCN代谢的贡献率模拟4.4. Simulation of the contribution rate of β-CAS and ST to KCN metabolism in rice seedlings
水稻幼苗对KCN的代谢量=β-CAS对KCN的代谢量+ST对KCN的代谢量,根据质量平衡得到以下物质平衡方程,作为水稻幼苗β-CAS和ST对KCN代谢的贡献率模型:The amount of metabolism of rice seedlings to KCN = the amount of metabolism of β-CAS to KCN + the amount of metabolism of ST to KCN, according to the mass balance, the following material balance equation is obtained, as the contribution rate model of rice seedlings β-CAS and ST to KCN metabolism:
式中,Mβ-CAS1、Mβ-CAS2、Mβ-CAS3分别表示3个KCN处理组水稻幼苗β-CAS对KCN的代谢量,单位是μg;MST1、MST2、MST3分别表示3个KCN处理组水稻幼苗ST对KCN的代谢量,单位是μg;MTotal1、MTotal2、MTotal3分别表示3个KCN处理组β-CAS和ST对KCN的总代谢量,单位是μg;In the formula, M β-CAS1 , M β-CAS2 , and M β-CAS3 represent the metabolism of β-CAS to KCN in three KCN-treated rice seedlings, respectively, in μg; M ST1 , M ST2 , and M ST3 represent 3 Metabolism of KCN by ST of rice seedlings in each KCN treatment group, the unit is μg; M Total1 , M Total2 , M Total3 represent the total metabolism of β-CAS and ST to KCN in the three KCN treatment groups, and the unit is μg;
M’β-CAS1、M’β-CAS2、M’β-CAS3分别表示3个ACC+KCN处理组水稻幼苗β-CAS对KCN的代谢量,单位是μg;M’ST1、M’ST2、M’ST3分别表示3个ACC+KCN处理组水稻幼苗ST对KCN的代谢量,单位是μg;M’Total1、M’Total2、M’Total3分别表示3个ACC+KCN处理组水稻幼苗β-CAS和ST对KCN的总代谢量,单位是μg。M' β-CAS1 , M' β-CAS2 , M' β-CAS3 represent the metabolism of β-CAS to KCN in three ACC+KCN treatment groups, respectively, the unit is μg; M' ST1 , M' ST2 , M ' ST3 represents the metabolic capacity of rice seedlings ST to KCN in the three ACC+KCN treatment groups, respectively, and the unit is μg; M' Total1 , M' Total2 , and M' Total3 represent the three ACC+KCN treatment groups, respectively, the β-CAS and Total metabolism of KCN by ST, in μg.
式(5)~式(7)为各KCN处理组水稻幼苗β-CAS与ST对KCN代谢的贡献模拟;式(8)~式(10)为各ACC+KCN处理组β-CAS与ST对KCN代谢的贡献模拟。Equations (5) to (7) are the simulations of the contribution of β-CAS and ST to KCN metabolism in rice seedlings of each KCN treatment group; Contribution simulation of KCN metabolism.
如图3所示,ACC+KCN处理组水稻幼苗β-CAS和ST基因的差异表达水平均高于KCN处理组。因此,构建水稻幼苗β-CAS和ST对KCN代谢的贡献率模型时认为ACC+KCN处理组水稻幼苗β-CAS和ST对KCN的代谢量均大于KCN处理组,即任意处理下均符合M’β-CAS>Mβ-CAS和M’ST>MST。As shown in Figure 3, the differential expression levels of β-CAS and ST genes in rice seedlings in the ACC+KCN treatment group were higher than those in the KCN treatment group. Therefore, when constructing the contribution rate model of rice seedlings β-CAS and ST to KCN metabolism, it is considered that the metabolism of β-CAS and ST to KCN in rice seedlings in ACC+KCN treatment group is greater than that in KCN treatment group, that is, under any treatment, it is consistent with M' β-CAS >M β-CAS and M' ST >M ST .
KCN通过ST代谢的路径会产生SCN-(化学计量比CN-∶SCN-=1∶1),而SCN-产生的过程中,部分SCN-也会被水稻幼苗代谢。因此,水稻幼苗体内产生的SCN-总量=SCN-的代谢量+SCN-的累积量。由此可以将式(5)~(10)转变为式(11)~(16):The pathway of KCN metabolism through ST will produce SCN - (stoichiometric ratio CN - : SCN - = 1:1), and in the process of SCN - production, part of SCN - will also be metabolized by rice seedlings. Therefore, the total amount of SCN - produced in rice seedlings = the metabolic amount of SCN - + the accumulated amount of SCN - . Thus, equations (5) to (10) can be transformed into equations (11) to (16):
其中,XST1、XST2、XST3分别表示3个KCN处理组水稻幼苗对SCN-的代谢量,单位是μg,X’ST1、X’ST2、X’ST3分别表示3个ACC+KCN处理组中水稻幼苗对SCN-的代谢量,单位是μg。Among them, X ST1 , X ST2 , and X ST3 represent the metabolism of SCN - in rice seedlings of the three KCN treatment groups, respectively, and the unit is μg, and X' ST1 , X' ST2 , and X' ST3 represent the three ACC+KCN treatment groups, respectively. Metabolism of SCN- by medium rice seedlings, in μg.
图7显示,在12h左右KCN在水稻水培全混生物反应器中的代谢已达到稳定极限状态,水稻幼苗体内SCN-的累积量也不再继续增加,即SCN-的产生与代谢之间达到平衡。以0.5μg为步长设置XST的值,如0.5、1、1.5...,n,将第48h测得的SCN-的累积量作为中间条件,当计算得到KCN处理组中β-CAS或ST对KCN的代谢量为最大值时即停止计算,此时,得到各步长下Mβ-CAS和MST的系列值。以0.5μg为步长设置X′ST的值,如0.5、1、1.5...,n,将第48h测得的SCN-的累积量作为中间条件,得到各步长下M’β-CAS和M’ST的系列值。Figure 7 shows that the metabolism of KCN in the rice hydroponic total mixed bioreactor has reached a stable limit at about 12 h, and the accumulation of SCN - in rice seedlings does not continue to increase, that is, the difference between the production and metabolism of SCN - reaches the limit. balance. Set the value of X ST with a step size of 0.5 μg, such as 0.5, 1, 1.5...,n, and take the accumulated amount of SCN - measured at the 48th hour as an intermediate condition, when the β-CAS or β-CAS in the KCN treatment group is calculated. The calculation was stopped when the metabolic amount of ST to KCN reached the maximum value. At this time, the series values of M β-CAS and M ST at each step were obtained. Set the value of X′ ST with a step size of 0.5μg, such as 0.5, 1, 1.5...,n, and use the accumulated amount of SCN - measured at the 48th h as an intermediate condition to obtain M′ β-CAS under each step size and series values of M'ST .
根据(17)和(18)的限定条件评估β-CAS和ST对KCN代谢的贡献率,根据这2个限定条件计算出2h和12h的β-CAS和ST对KCN的代谢量,如表7所示,计算公式如下:According to the qualifications of (17) and (18), the contribution rate of β-CAS and ST to KCN metabolism was evaluated, and the metabolism of β-CAS and ST to KCN at 2h and 12h was calculated according to these 2 qualifications, as shown in Table 7. As shown, the calculation formula is as follows:
上述限定条件表示,在不同外源KCN胁迫浓度处理下均要满足ACC+KCN处理组中β-CAS(ST)对KCN代谢量(μg)均要大于KCN处理组中β-CAS(ST)对KCN代谢量(μg)。The above limiting conditions indicate that under different exogenous KCN stress concentrations, the metabolic amount (μg) of β-CAS(ST) to KCN in the ACC+KCN treatment group is greater than that of β-CAS(ST) in the KCN treatment group. KCN metabolism (μg).
表7水稻幼苗β-CAS和ST对KCN代谢的贡献率估计Table 7 Estimation of contribution rate of β-CAS and ST to KCN metabolism in rice seedlings
从表7可以得到:(1)在不同浓度外源KCN胁迫下,β-CAS对KCN的代谢效率总是高于ST;(2)在不同浓度外源KCN胁迫下,β-CAS和ST对KCN的代谢贡献率范围基本相似;(3)随着胁迫时间的推移,β-CAS对KCN的代谢效率增加而ST对KCN的代谢效率降低,这应该是ST对KCN的敏感性所致。解决这一问题,有利于后续评估水稻对KCN修复效率。It can be obtained from Table 7: (1) Under different concentrations of exogenous KCN stress, the metabolic efficiency of β-CAS to KCN is always higher than that of ST; (2) Under different concentrations of exogenous KCN stress, β-CAS and ST The metabolic contribution rate range of KCN was basically similar; (3) With the passage of stress time, the metabolic efficiency of β-CAS to KCN increased while that of ST decreased, which should be due to the sensitivity of ST to KCN. Solving this problem is beneficial to the subsequent evaluation of the KCN repair efficiency of rice.
需要说明的是,在本申请中,诸如第一、第二等之类的关系术语仅仅用来将一个实体或者操作与另一个实体或操作区分开来,而不一定要求或者暗示这些实体或操作之间存在任何这种实际的关系或者顺序。而且,术语“包括”、“包含”或者其任何其他变体意在涵盖非排他性的包含,从而使得包括一系列要素的过程、方法、物品或者设备不仅包括那些要素,而且还包括没有明确列出的其他要素,或者是还包括为这种过程、方法、物品或者设备所固有的要素。在没有更多限制的情况下,由语句“包括一个……”限定的要素,并不排除在包括所述要素的过程、方法、物品或者设备中还存在另外的相同要素。It should be noted that in this application, relational terms such as first, second, etc. are only used to distinguish one entity or operation from another entity or operation, and do not necessarily require or imply these entities or operations There is no such actual relationship or order between them. Moreover, the terms "comprising", "comprising" or any other variation thereof are intended to encompass a non-exclusive inclusion such that a process, method, article or device comprising a list of elements includes not only those elements, but also includes not explicitly listed or other elements inherent to such a process, method, article or apparatus. Without further limitation, an element qualified by the phrase "comprising a..." does not preclude the presence of additional identical elements in a process, method, article or apparatus that includes the element.
本说明书中的各个实施例均采用相关的方式描述,各个实施例之间相同相似的部分互相参见即可,每个实施例重点说明的都是与其他实施例的不同之处。Each embodiment in this specification is described in a related manner, and the same and similar parts between the various embodiments may be referred to each other, and each embodiment focuses on the differences from other embodiments.
以上所述仅为本发明的较佳实施例而已,并非用于限定本发明的保护范围。凡在本发明的精神和原则之内所作的任何修改、等同替换、改进等,均包含在本发明的保护范围内。The above descriptions are only preferred embodiments of the present invention, and are not intended to limit the protection scope of the present invention. Any modification, equivalent replacement, improvement, etc. made within the spirit and principle of the present invention are included in the protection scope of the present invention.
Claims (9)
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN202111383400.1A CN114333988A (en) | 2021-11-22 | 2021-11-22 | Estimation method for the contribution rate of plant β-CAS and ST to KCN metabolism |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN202111383400.1A CN114333988A (en) | 2021-11-22 | 2021-11-22 | Estimation method for the contribution rate of plant β-CAS and ST to KCN metabolism |
Publications (1)
Publication Number | Publication Date |
---|---|
CN114333988A true CN114333988A (en) | 2022-04-12 |
Family
ID=81046361
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN202111383400.1A Pending CN114333988A (en) | 2021-11-22 | 2021-11-22 | Estimation method for the contribution rate of plant β-CAS and ST to KCN metabolism |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN114333988A (en) |
Citations (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US20150020239A1 (en) * | 2013-06-26 | 2015-01-15 | Symbiota, Inc. | Seed-origin endophyte populations, compositions, and methods of use |
US20180213800A1 (en) * | 2015-06-26 | 2018-08-02 | Indigo Ag, Inc. | Penicillium endophyte compositions and methods for improved agronomic traits in plants |
CN109880877A (en) * | 2017-12-06 | 2019-06-14 | 中国科学院大连化学物理研究所 | A metabolomics-based method for evaluating the toxic effects of low-dose combined exposure to organic pollutants |
CN112820352A (en) * | 2020-12-28 | 2021-05-18 | 桂林理工大学 | Screening method for chemical regulators based on regulating gene expression in stressed plants |
-
2021
- 2021-11-22 CN CN202111383400.1A patent/CN114333988A/en active Pending
Patent Citations (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US20150020239A1 (en) * | 2013-06-26 | 2015-01-15 | Symbiota, Inc. | Seed-origin endophyte populations, compositions, and methods of use |
US20180213800A1 (en) * | 2015-06-26 | 2018-08-02 | Indigo Ag, Inc. | Penicillium endophyte compositions and methods for improved agronomic traits in plants |
CN109880877A (en) * | 2017-12-06 | 2019-06-14 | 中国科学院大连化学物理研究所 | A metabolomics-based method for evaluating the toxic effects of low-dose combined exposure to organic pollutants |
CN112820352A (en) * | 2020-12-28 | 2021-05-18 | 桂林理工大学 | Screening method for chemical regulators based on regulating gene expression in stressed plants |
Non-Patent Citations (2)
Title |
---|
C.-Z. LI: "Mathematical modularization of the contribution of β-cyanoalanine synthase and sulfurtransferase to cyanide assimilation in rice plants", 《INTERNATIONAL JOURNAL OF ENVIRONMENTAL SCIENCE AND TECHNOLOGY》, vol. 20, 29 April 2023 (2023-04-29) * |
季静;柳洁;王罡;杜希龙;曹海燕;荣非;金超: "玉米氰化物解毒基因β-CAS和NIT在非生物胁迫下的表达与生物学效应", 天津大学学报, no. 005, 31 December 2015 (2015-12-31) * |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
Iqbal et al. | Organic manure coupled with inorganic fertilizer: An approach for the sustainable production of rice by improving soil properties and nitrogen use efficiency | |
Bhattacharyya et al. | Mechanism of plant mediated methane emission in tropical lowland rice | |
Alhaj Hamoud et al. | Effect of irrigation regimes and soil texture on the potassium utilization efficiency of rice | |
Javed et al. | Seed coating in direct seeded rice: An innovative and sustainable approach to enhance grain yield and weed management under submerged conditions | |
Lahlali et al. | High-throughput molecular technologies for unraveling the mystery of soil microbial community: challenges and future prospects | |
CN107066823A (en) | Based on plant, soil, microorganism heavy-metal contaminated soil repairing effect integrated evaluating method | |
Katayanagi et al. | Validation of the DNDC-Rice model to discover problems in evaluating the nitrogen balance at a paddy-field scale for single-cropping of rice | |
Hakla et al. | Gibberellins target shoot-root growth, morpho-physiological and molecular pathways to induce cadmium tolerance in Vigna radiata L. | |
CN111398548A (en) | A prediction method of nitrogen and phosphorus concentration in surface flow wetland water based on plant action | |
El-Shal et al. | Effect of nano-fertilizers on alfalfa plants grown under different salt stresses in hydroponic system | |
Yang et al. | Grazing affects bacterial and fungal diversities and communities in the rhizosphere and endosphere compartments of leymus chinensis through regulating nutrient and ion distribution | |
Ma et al. | Increasing methane (CH4) emissions and altering rhizosphere microbial diversity in paddy soil by combining Chinese milk vetch and rice straw | |
Fu et al. | Critical transition of soil microbial diversity and composition triggered by plant rhizosphere effects | |
van Keulen | (Tropical) soil organic matter modelling: problems and prospects | |
Javeed et al. | Biochar enriched with buffalo slurry improved soil nitrogen and carbon dynamics, nutrient uptake and growth attributes of wheat by reducing leaching losses of nutrients | |
Wang et al. | Research progress in crop root biology and nitrogen uptake and use, with emphasis on cereal crops | |
Xu et al. | The effects of cultivation patterns and nitrogen levels on fertility and bacterial community characteristics of surface and subsurface soil | |
Dong et al. | Silicon fertilizer addition can improve rice yield and lodging traits under reduced nitrogen and increased density conditions | |
Yang et al. | Exploring the effect of different application rates of biochar on the accumulation of nutrients and growth of flue-cured tobacco (Nicotiana tabacum) | |
Davidson et al. | An investigation of non-steady-state algal growth. I. An experimental model ecosystem. | |
Huang et al. | Effects of on-and off-year management practices on the soil organic C fractions and microbial community in a Moso bamboo (Phyllostachys edulis) forest in subtropical China | |
CN114333988A (en) | Estimation method for the contribution rate of plant β-CAS and ST to KCN metabolism | |
Egelkraut et al. | Predicting N mineralized in a Georgia Coastal Plain field | |
Huang et al. | Effects of Carbon-Based Modified Materials on Soil Water and Fertilizer Retention and Pollution Control in Rice Root Zone | |
Wang et al. | Effects of nitrogen stress and nitrogen form ratios on the bacterial community and diversity in the root surface and rhizosphere of Cunninghamia lanceolata and Schima superba |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
PB01 | Publication | ||
PB01 | Publication | ||
SE01 | Entry into force of request for substantive examination | ||
SE01 | Entry into force of request for substantive examination |