CN109121988A - A kind of research that heavy metal cadmium stress influences daphne odera characteristic - Google Patents

A kind of research that heavy metal cadmium stress influences daphne odera characteristic Download PDF

Info

Publication number
CN109121988A
CN109121988A CN201811137494.2A CN201811137494A CN109121988A CN 109121988 A CN109121988 A CN 109121988A CN 201811137494 A CN201811137494 A CN 201811137494A CN 109121988 A CN109121988 A CN 109121988A
Authority
CN
China
Prior art keywords
daphne odera
plant
soil
concentration
stress
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
Application number
CN201811137494.2A
Other languages
Chinese (zh)
Inventor
公维昌
刘艳红
陈亚青
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Honghe University
Original Assignee
Honghe University
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 Honghe University filed Critical Honghe University
Priority to CN201811137494.2A priority Critical patent/CN109121988A/en
Publication of CN109121988A publication Critical patent/CN109121988A/en
Pending legal-status Critical Current

Links

Classifications

    • AHUMAN NECESSITIES
    • A01AGRICULTURE; FORESTRY; ANIMAL HUSBANDRY; HUNTING; TRAPPING; FISHING
    • A01GHORTICULTURE; CULTIVATION OF VEGETABLES, FLOWERS, RICE, FRUIT, VINES, HOPS OR SEAWEED; FORESTRY; WATERING
    • A01G17/00Cultivation of hops, vines, fruit trees, or like trees
    • A01G17/005Cultivation methods

Landscapes

  • Life Sciences & Earth Sciences (AREA)
  • Botany (AREA)
  • Environmental Sciences (AREA)
  • Cultivation Of Plants (AREA)

Abstract

A kind of research that heavy metal cadmium stress influences daphne odera characteristic, the present invention relates to heavy metal technical research technical fields;The preparation of experimental material;Test method;Data processing;Interpretation of result;Research conclusion;Daphne odera under Cd stress does not occur death and is poisoned phenomenon, shows stronger vitality, and intracorporal antioxidase is induced to protect plant cell not coerced to eliminate destruction of the active oxygen generated to cell membrane;Every chlorophyll fluorescence parameters also reflect daphne odera and are not affected by the larger stress of cadmium, can be normally carried out photosynthesis;When being measured to the intracorporal cadmium content of daphne odera, there is certain Cd accumulation amount in root, stem and leaf, but the standard of Cd-hyperaccumulator is not reached, it is not belonging to Cd-hyperaccumulator, daphne odera described above is under the stress of cadmium, energy normal growth, the normal Scavenger of ROS of internal antioxidase energy, photosynthesis is not affected by influence, with certain extracting accumulation ability and has stronger tolerance to cadmium in soil.

Description

A kind of research that heavy metal cadmium stress influences daphne odera characteristic
Technical field
The present invention relates to heavy metal technical research technical fields, and in particular to a kind of heavy metal cadmium stress is to daphne odera characteristic The research of influence.
Background technique
Industrial technology also brings a large amount of environmental pollution to the mankind while pushing human civilization process, wherein with Heavy metal pollution is the most prominent, and cadmium pollution is the most serious in heavy metal pollution.In " the national soil that 2014 announce Survey of contaminating status bulletin " in, the cadmium pollution exceeding standard rate in China soil is higher than most inorganic pollution up to 7.0%, dirty Area covering China major part soil is contaminated, and this area just rises year by year.
Cadmium is the non-essential element in growing process, has strong toxicity, is not easy to be degraded in the soil and easy quilt Plant absorption is simultaneously accumulated in internal feature, can cause serious harm to animals and plants and the mankind by food chain.In recent years, people Internal feature can be absorbed by plants and is accumulated in using cadmium, soil pollution is repaired, and find to cadmium have it is resistance to It is made some progress during property and hyperaccumulation plant.It is reported that there is hyperaccumulation or patience to cadmium Plant is largely focused in composite family, grass family, Cruciferae, Cyperaceae and Crassulaceae, such as black nightshade, Indian mustard, Golconda Violet, trade route etc., however, these super enriching plants generally have the characteristics that few germplasm resource, slow growth and repair phase length, It is unfavorable for large area to use and promote.Therefore, the super enriching plant that germplasm resource is wide, the speed of growth is fast, remediation efficiency is high is found It is the key that one of plant soil restoration.
In China, the plant that Lindley Butterflybush Herb belongs to is distributed mainly on southwestern, northwest and Central-South there are about 30 kinds or more (including mutation) Equal areas, and it is most wide with southwestern Area distribution, with regard to all up to 27 kinds of Yunnan, it is grown in arid, barren area mostly, there is kind Plant resource distribution is wide, growth of seedling speed is fast, it is drought-resistant, adapt to environment strong feature.Studies have shown that mutual leaf Lindley Butterflybush Herb is not only Stronger adaptability is shown to arid, also there is very strong tolerance to cadmium, and have higher bioaccumulation ability.Daphne odera Belong to a kind of shrub or dungarunga in Lindley Butterflybush Herb category.Daphne odera is the dispersed species in Asia, is mainly distributed on height above sea level in 200- The river bank 3000m or the woods side habitat Deng Yirao, and can be grown in barren environment.Daphne odera has narrow and long raceme, It is born in an end and axil;Corolla pipe tubulose, corolla white, fragrance (linalool content up to 85%);Stamen it is raw in corolla pipe Middle part;The month at florescence 1-10;The fruiting period 3-12 month, and the daphne odera speed of growth is fast, is typical resistance to trimming plant.Therefore, seven are studied In perfume (or spice) under the stress of cadmium, growth characters, fluorescent characteristic and the enrichment condition to cadmium, to judge whether daphne odera can be used for The reparation of soil pollution can provide certain contribution for the reparation of environmental pollution caused by heavy metal cadmium.
Summary of the invention
In view of the defects and deficiencies of the prior art, the present invention intends to provide a kind of structure is simple, design rationally, make The research influenced on daphne odera characteristic is coerced with convenient heavy metal cadmium, itself can be adjusted by obtaining daphne odera under Cd is coerced Defense mechanism reduces the damage of physiological metabolism, has preferable patience to Cd, can in Cd contaminated soil normal growth, and have There is certain repair ability, has preferable exploitation and with prospect.
To achieve the above object, the technical solution adopted by the present invention is that: its research method is as follows:
1, the preparation of experimental material
1.1, vegetable material is annual daphne odera seedling;
It 1.2, is the red soil for not cultivating crop for examination soil;
1.3, agents useful for same is cadmium nitrate (Cd (NO3)2·4H2O), analyze pure;
2, test method
2.1, soil potted plant experiment: taking appropriate soil, after natural air drying, hammer are broken, with Cd2+Solution is uniformly mixed and divides It is not fitted into bag, every part of 10kg, Cd is set2+Concentration gradient is 0 (CK), 25,50,100,200,400mg/kg, Cd work is not added For control, 5 repetitions of each processing, cultivating bag bottom is entangled with polybag, is balanced 14 days, after balance period, chooses plant height phase Closely, stem thickness is close, daphne odera seedling similar in leaf blade size and quantity and is transplanted in experiment basin, after plantation three months, carries out phase The measurement of index is closed, during soil is balanced and planted, it is ensured that the water content of soil is 60% or so;
2.2, the measurement of physical signs: the vitality test of superoxide dismutase uses nitroblue tetrazolium colorimetric method, hydrogen peroxide The measurement of enzyme activity is measured using ultraviolet absorption method, the measurement of peroxidase activity is surveyed using guaiacol method Fixed, mda content measurement is measured using thiobarbituricacidα- method;
2.3, the measurement of photosynthetic parameters the measurement of chlorophyll fluorescence parameters: is carried out using the portable photosynthetic instrument of Li-6400;? The evening 21:00-22:00 of fine day, when measurement, use leaf chamber size for 3 × 2cm2, light source used, temperature, humidity, carbon dioxide Concentration is that under natural conditions, location parameter is initial fluorescence, maximum fluorescence, steady state fluorescence, fluorescence rises to can change thylakoid Maximum fluorescence, and II maximal photochemistry efficiency of PS, non-photochemistry fluorescent quenching coefficient, the practical Photochemical Efficiency of PS II are calculated, it counts It is as follows to calculate formula:
II maximal photochemistry efficiency of PS: Fv/Fm=(Fm-Fo)/Fm
Non- photochemistry fluorescent quenching coefficient: NPQ=(Fm-Fm')/Fm'
The practical Photochemical Efficiency of PS II: Φ PSII=(Fm'-Fs)/Fm', wherein F0 is initial fluorescence, Fm is maximum glimmering Light, Fs are steady state fluorescence, Fm ' be fluorescence rise to can change thylakoid maximum fluorescence, Fv/Fm be II maximal photochemistry efficiency of PS, NPQ is non-photochemistry fluorescent quenching coefficient, Φ PSII is the practical Photochemical Efficiency of PS II;
2.4, the measurement of heavy metal cadmium content: root, stem, leaf sample after plantation three months, after weighing 0.2g drying respectively Afterwards, it crushes, the sieving of 100 mesh, 8ml digestion solution is added, the concentration of digestion solution is HNO3∶H2O2=6: 2, it is placed in microwave dissolver It is cleared up;It clears up and is cooled to room temperature completely to material, dilute HNO is added3After constant volume, surveyed using flame atomic absorption spectrometry Cd content in plant material, replication 3 times, and calculate TF, that is, transhipment coefficient and and BCF, that is, concentration coefficient:
Transhipment coefficient=aerial part cadmium content/root that is averaged is averaged cadmium content
Root bio-concentration factor=root is averaged the content of cadmium in cadmium content/soil
Aerial part bio-concentration factor=aerial part is averaged the content of cadmium in cadmium content/soil;
3, data processing
Data processing is carried out using Origin 8.5 and Past 2.08;
4, interpretation of result
4.1, influence of the various concentration Cd processing to the vigor and mda content of daphne odera antioxidase:
Under the stress of Cd, peak occur when the intracorporal SOD vigor of daphne odera is under 100mg/kg soil Cd stress is Difference that there are no significant under 425.15 ± 2.41U/g, remaining Cd stress, and substantially less than control group;The energy value of POD exists Maximum value occurs in 25mg/kg soil Cd when coercing be 137.24 ± 1.37U/ (gmin), and year-on-year control group increases 38.96%, minimum value occurs in soil Cd level when being 400mg/kg be 43.91 ± 1.61U/ (gmin), year-on-year control group drop Low 55.54%;There is 0.87 ± 0.03U/ of maximum value (gmin) when being 100mg/kg in the vigor soil Cd of CAT, compares on year-on-year basis Group increases 19.18%, difference that there are no significant under remaining Cd stress;SOD, POD, CAT 400mg/kg soil Cd stress under, Vigor is below control group, and year-on-year control group has dropped 16.75%, 55.54%, 5.48% respectively.Daphne odera is at Cd stress In reason, its active oxygen metabolism of vigor energy normal regulating balance of internal each antioxidase, protection plant preserves from, has to Cd There is stronger tolerance.
The content of MDA is gradually decreased with the increase of soil Cd concentration, and integral level is lower than control group;MDA content is in Cd There is 0.33 ± 0.005 μm of ol/g of minimum value when being 100mg/kg in concentration for the treatment of, and year-on-year control group reduces 32.65%;In Cd Concentration for the treatment of be 400mg/kg when, content be 0.42 ± 0.005 μm of ol/, still lower than control group 18.37%.Daphne odera blade Interior Lipid peroxidation metabolism degree is lower, and the film rouge in blade is not affected by injury, and daphne odera has stronger tolerance to Cd;
4.2, influence of the Cadmium treated of various concentration to daphne odera fluorescent characteristic:
When soil Cd concentration is 25mg/kg, daphne odera appearance maximum Fv/Fm value, 0.87 ± 0.02, it is higher than control group 1.16%;Minimum value appear in Cd concentration be 400mg/kg when, lower than control group 4.65%.The Fv/Fm value of daphne odera between Between 0.82-0.87, meet the normal range (NR) of general plant.This explanation, daphne odera is under Cd stress in its photosynthetic organs PSII is not affected by damage.
The NPQ value of daphne odera is gradually increasing with the raising of soil Cd concentration, and maximum value appears in Cd concentration for the treatment of and is When 400mg/kg, 0.45 ± 0.07, higher than control group by 80.00%, minimum value then appears in control group, and 0.25 ± 0.02.Seven In light protective capability in fragrant Photosynthetic, can enhance with the raising of soil Cd concentration, and photosynthetic organs are not affected by damage, plant Object can be normally carried out photosynthesis.
There is maximum value under the Cd stress of 25mg/kg in the Φ PSII value of daphne odera, higher than control group by 1.0%, remaining side of body Difference that there are no significant under compeling, daphne odera is under Cd stress, and intracorporal smooth protective capability enhancing, photosynthetic organs are not by light Stress, each photosynthetic process are not affected by influence, and photosynthesis can be normally carried out, and also be not affected by shadow to the fixation and assimilative capacicy of carbon It rings;
4.3, heavy metal Cd is in the intracorporal distribution of daphne odera and enrichment characteristics:
With the raising of heavy metal Cd concentration, the root of daphne odera, stem, also conspicuousness rises the Cd content being enriched in leaf therewith, Its different parts is different to the accumulation characteristic of Cd, when soil Cd level is between 0-50mg/kg, aerial part (stem+leaf) enrichment Cd ability be higher than subterraneous root;When soil Cd level is higher than 100mg/kg, subterraneous root is enriched with Cd speed and is higher than aerial part, With the increase of soil Cd concentration, the Cd content of daphne odera aerial part and under ground portion enrichment is continuously increased;The ground of daphne odera It is respectively 77.92 ± 1.20mg/kg that the Cd content of upper part and root enrichment, which has maximum value in the Cd stress of 400mg/kg, With 111.63 ± 6.94mg/kg, the Cd in environment can be constantly absorbed into the internal of plant by daphne odera, and with soil Cd concentration Increase and is continuously improved;
For soil Cd concentration in 0-50mg/kg, daphne odera is greater than 1 (1.19 ± 0.18-1.91 to the transhipment coefficient (TF) of Cd ±0.25);With the increase of soil Cd concentration, especially when soil Cd level is higher than 100mg/kg, daphne odera turns Cd Transporting coefficient, there was no significant difference less than 1 (0.7 ± 0.14-0.74 ± 0.08), and between various concentration processing;This illustrates that daphne odera can The heavy metal Cd of effective transfer root enrichment, aerial part bio-concentration factor and root bio-concentration factor are in 25mg/kg soil Maximum value 1.58 ± 0.04 and 1.38 ± 0.21 is respectively provided with when earth Cd, but significant with the raising of heavy metal Cd concentration for the treatment of It reduces, illustrates daphne odera under Cd stress, can constantly extract the heavy metal Cd in soil, but it extracts ability with soil Cd water Flat raising constantly reduces, and has maximum extracting ability when soil Cd concentration is 25mg/kg;;
5, discussion of results
5.1, under the stress of heavy metal Cd daphne odera leaf antioxidase response and protection mechanism:
When plant is coerced by arid, high temperature, low temperature and heavy metal etc., a large amount of active oxygen can generate in vivo, no Secondary stress is generated to plant after disconnected accumulation, makes the Lipid peroxidation metabolism of cell membrane, damages the cell membrane of plant;Antioxidant Enzymes System, be one of plant defense system, wherein SOD enzyme is the first barrier of Antioxidant Enzyme Systems, it by catalysis super oxygen yin from Sub- free radical O2 ?It is converted into H202With the reaction of ground state oxygen, a large amount of superoxide anion is removed, cell is avoided to come to harm, super oxygen Anion is converted into H202After ground state oxygen, the H of generation202It also can be to cell damage.POD enzyme and CAT enzyme can be by H202It urges Change is decomposed into water and oxygen, protects plant cell, and when plant is in stress or organ senescence, cell death, antioxidase is removed The rate of active oxygen can cause the Lipid peroxidation metabolism degree of cell membrane to enhance, final product malonaldehyde lower than the rate that it is generated Content also rise with it, therefore, the height of MDA content can reflect the Lipid peroxidation metabolism degree of cell.In this study, in seven Fragrant SOD enzyme activity in vivo and CAT enzyme activity do not occur significantly improving with the increase of Cd concentration, and POD enzyme activity is then with Cd's Concentration increase first rises to be declined afterwards, this is similar to the experimental result on current beans seed in office;Moreover, MDA in daphne odera leaf Content is integrally lower than control group, illustrates under Cd stress, and cell membrane is not affected by injury, and antioxidase can be effectively protected seven In spiceleaf piece injured from Lipid peroxidation metabolism, daphne odera has very strong tolerance to heavy metal Cd;
5.2, under the stress of heavy metal Cd daphne odera chlorophyll fluorescence variation:
In plant chlorophyll fluorescence kinetics, the situation of change of every chlorophyll fluorescence parameters index can reflect and take the post as On influence photosynthetic in plant, Fv/Fm value reflects the degree of impairment of plant PS II for what adverse circumstance, the non-stress the case where Under, which not will receive the influence of species and growth conditions, be generally stabilized between 0.80-0.85, and therefore, which can also be anti- Mirror whether plant is forced, NPQ value is non-photochemistry fluorescent quenching coefficient, and the size of value reflects PSII reaction center Antenna beam consume excessive energy by improving non-radiation type heat dissipation after absorbing excessive luminous energy, protect photosynthetic The ability of mechanism damage is strong and weak, belongs to a kind of self-protective mechanism of plant, when plant is forced, non-photochemistry is glimmering Optical quenching coefficient NPQ, that is, plant light protective capability will appear variation, and value is bigger, and the light protective capability for indicating plant is stronger, phase The practical Photochemical Efficiency Φ PSII value of the PSII answered can be also varied, and Φ PSII indicates the practical Photochemical Efficiency of PSII, value Size represent the power of plant assimilating power, be worth bigger, the assimilatory power of plant is bigger, and the fixation and assimilative capacicy to carbon are also got over By force, in this study, the value of Fv/Fm and Φ PSII first rises and declines afterwards with the rising of cadmium concentration, the value of NPQ then constantly on Rise, this at present research annual fleabane herb various concentration Cd stress under the result of Chlorophyll Fluorescence it is similar, illustrate in seven For perfume (or spice) under Cd stress, intracorporal optical protection mechanism preferably protects photosynthetic organs, can carry out normal photosynthetic work With being not affected by the stress of cadmium;
5.3, heavy metal Cd coerces enrichment and the transfer characteristic of lower daphne odera:
Plant refers in the Heavy-metal Polluted Environment of high concentration that plant remains to normal growth to the patience of heavy metal, and It is not affected by apparent damage, and has a certain amount of heavy metal in vivo;Super enriching plant refers to that plant can utilize itself all kinds of mechanism, Heavy metal excess in environment is absorbed and is transported to aboveground vegetation part, and different heavy metals, to super enriching plant Definition is also different, and cadmium enriching plant refers to that the aerial part cadmium content of plant has to be larger than 100mg/kg, and transhipment coefficient reflects Transhipment complexity of certain element from plant root to aboveground vegetation part, bio-concentration factor then reflect it to heavy metal Accumulation ability power, in this study, daphne odera under the processing of each cadmium concentration, can normal growth, and and control group Without obvious morphological differences;After measured, intracorporal cadmium content is not up to the standard of Cd-hyperaccumulator, is not belonging to the plant of cadmium super enrichment Object, but stronger tolerance and enrichment transfer ability are shown to cadmium;
6, research conclusion
In this study, the daphne odera under Cd stress does not occur death and is poisoned phenomenon, shows stronger vitality, Intracorporal antioxidase is induced to protect plant cell not coerced to eliminate destruction of the active oxygen generated to cell membrane;Respectively Item chlorophyll fluorescence parameters also reflect daphne odera and are not affected by the larger stress of cadmium, can be normally carried out photosynthesis;To seven In fragrant intracorporal cadmium content have certain Cd accumulation amount in root, stem and leaf when being measured, but do not reach Cd-hyperaccumulator Standard, be not belonging to Cd-hyperaccumulator, daphne odera described above under the stress of cadmium, can normal growth, in vivo it is anti-oxidant The normal Scavenger of ROS of enzyme energy, photosynthesis are not affected by influence, have certain enrichment to cadmium and have stronger tolerance.
After adopting the above method, the invention has the following beneficial effects: a kind of heavy metal cadmium stress of the present invention is to daphne odera The research that characteristic influences, obtains the daphne odera under Cd stress and does not occur death and be poisoned phenomenon, show stronger vitality, Intracorporal antioxidase is induced to protect plant cell not coerced to eliminate destruction of the active oxygen generated to cell membrane;Respectively Item chlorophyll fluorescence parameters also reflect daphne odera and are not affected by the larger stress of cadmium, can be normally carried out photosynthesis;To seven In fragrant intracorporal cadmium content have certain Cd accumulation amount in root, stem and leaf when being measured, but do not reach Cd-hyperaccumulator Standard, be not belonging to Cd-hyperaccumulator, daphne odera described above under the stress of cadmium, can normal growth, in vivo it is anti-oxidant The normal Scavenger of ROS of enzyme energy, photosynthesis are not affected by influence, have certain extracting accumulation ability to cadmium in soil and have Stronger tolerance.
Detailed description of the invention
In order to more clearly explain the embodiment of the invention or the technical proposal in the existing technology, to embodiment or will show below There is attached drawing needed in technical description to be briefly described, it should be apparent that, the accompanying drawings in the following description is only this Some embodiments of invention for those of ordinary skill in the art without creative efforts, can be with It obtains other drawings based on these drawings.
Fig. 1 be in the present invention Cd to the effect of vigor chart of daphne odera blade MDA (with there is an identical small letter after column data Letter, indicate not significant (One-way ANOVA) in 5% horizontal upper difference.
Fig. 2 be in the present invention Cd to the effect of vigor chart of daphne odera foliar SOD (with there is an identical small letter after column data Letter, indicate not significant (One-way ANOVA) in 5% horizontal upper difference.
Fig. 3 be in the present invention Cd to the effect of vigor chart of daphne odera blade POD (with there is an identical small letter after column data Letter, indicate not significant (One-way ANOVA) in 5% horizontal upper difference.
Fig. 4 is that Cd influences chart (with there is an identical small letter after column data to the content of daphne odera blade CAT in the present invention Letter, indicate not significant (One-way ANOVA) in 5% horizontal upper difference.
Fig. 5 is that difference Cd concentration handles lower daphne odera blade PSII Photochemical Efficiency parameter list (same column data in the present invention There is an identical lowercase afterwards, indicates not significant (One-way ANOVA) in 5% horizontal upper difference.
Fig. 6 is that various concentration handles lower Cd in the intracorporal distribution of daphne odera and transhipment coefficient and concentration coefficient in the present invention Situation table (with there is an identical lowercase after column data, is indicated in the 5% horizontal not significant (One-way of upper difference ANOVA)。
Specific embodiment
The present invention will be further described below with reference to the drawings.
Referring to as shown in figs 1 to 6, present embodiment the technical solution adopted is that: its research method is as follows:
1, the preparation of experimental material
1.1, vegetable material is annual daphne odera seedling, is adopted in Yunnan Province Gejiu;
It 1.2, is the red soil for not cultivating crop for examination soil;
1.3, agents useful for same is cadmium nitrate (Cd (NO3)2·4H2O), analyze pure;
2, test method
2.1, soil potted plant experiment: taking appropriate soil, after natural air drying, hammer are broken, with Cd2+Solution is uniformly mixed and divides It is not fitted into bag (non-woven fabrics planting bag), every part of 10kg, Cd is set2+Concentration gradient is 0 (CK), 25,50,100,200,400mg/ Kg (is added) in the form of cadmium nitrate, Cd is not added as control, 5 repetitions of each processing, cultivating bag bottom plastic bag cover Firmly, it balances 14 days, after balance period, chooses that plant height is close, stem thickness is close, daphne odera seedling similar in leaf blade size and quantity and moves It plants in experiment basin, after plantation three months, the measurement of index of correlation is carried out, during soil is balanced and planted, it is ensured that soil Water content is 60% or so;
2.2, the measurement of physical signs: the vitality test of superoxide dismutase (SOD) uses nitroblue tetrazolium (NBT) colorimetric The measurement of method, catalase (CAT) vigor is measured using ultraviolet absorption method, the measurement of peroxidase (POD) vigor It is measured using guaiacol method, the measurement of malonaldehyde (MDA) content is measured using thiobarbituricacidα- method;
2.3, the measurement of chlorophyll fluorescence parameters: the portable photosynthetic instrument (production of Li-COR company of the U.S.) of Li-6400 is used Carry out the measurement of photosynthetic parameters;Use leaf chamber size for 3 × 2cm in the evening 21:00-22:00 of fine day, measurement2, used up Source, temperature, humidity, gas concentration lwevel be under natural conditions, location parameter be initial fluorescence, maximum fluorescence, steady state fluorescence, Fluorescence, which rises to, can change thylakoid maximum fluorescence, and calculate II maximal photochemistry efficiency of PS, non-photochemistry fluorescent quenching coefficient, PS II practical Photochemical Efficiency, calculation formula are as follows:
II maximal photochemistry efficiency of PS (Fv/Fm)=(Fm-Fo)/Fm
Non- photochemistry fluorescent quenching coefficient (NPQ)=(Fm-Fm')/Fm'
The practical Photochemical Efficiency of PS II (Φ PSII)=(Fm'-Fs)/Fm', wherein F0 is initial fluorescence, Fm is maximum glimmering Light, Fs are steady state fluorescence, Fm ' be fluorescence rise to can change thylakoid maximum fluorescence, Fv/Fm be II maximal photochemistry efficiency of PS, NPQ is non-photochemistry fluorescent quenching coefficient, Φ PSII is the practical Photochemical Efficiency of PS II;
2.4, the measurement of heavy metal cadmium content: root, stem, leaf sample after plantation three months, after weighing 0.2g drying respectively Afterwards, it crushes, the sieving of 100 mesh, 8ml digestion solution is added, the concentration of digestion solution is HNO3∶H2O2=6: 2, it is placed in microwave dissolver It is cleared up;It clears up and is cooled to room temperature completely to material, dilute HNO is added3After constant volume, surveyed using flame atomic absorption spectrometry Cd content in plant material, replication 3 times, and calculate TF, that is, transhipment coefficient and and BCF, that is, concentration coefficient:
Transhipment coefficient (TF)=aerial part cadmium content (mg/kg)/root that is averaged is averaged cadmium content (mg/kg)
Root bio-concentration factor (BCF)=root is averaged the content (mg/kg) of cadmium in cadmium content (mg/kg)/soil
Aerial part bio-concentration factor (BCF)=aerial part is averaged the content of cadmium in cadmium content (mg/kg)/soil (mg/kg);
3, data processing
Data processing is carried out using Origin 8.5 and Past 2.08;
4, interpretation of result
4.1, influence of the various concentration Cd processing to the vigor and mda content of daphne odera antioxidase:
Under the stress of Cd, peak occur when the intracorporal SOD vigor of daphne odera is under 100mg/kg soil Cd stress is Difference that there are no significant under 425.15 ± 2.41U/g, remaining Cd stress, and substantially less than control group;The energy value of POD exists Maximum value occurs in 25mg/kg soil Cd when coercing be 137.24 ± 1.37U/ (gmin), and year-on-year control group increases 38.96%, minimum value occurs in soil Cd level when being 400mg/kg be 43.91 ± 1.61U/ (gmin), year-on-year control group drop Low 55.54%;There is 0.87 ± 0.03U/ of maximum value (gmin) when being 100mg/kg in the vigor soil Cd of CAT, compares on year-on-year basis Group increases 19.18%, difference that there are no significant under remaining Cd stress;SOD, POD, CAT 400mg/kg soil Cd stress under, Vigor is below control group, and year-on-year control group has dropped 16.75%, 55.54%, 5.48% respectively.Daphne odera is at Cd stress In reason, its active oxygen metabolism of vigor energy normal regulating balance of internal each antioxidase, protection plant preserves from, has to Cd There is stronger tolerance.
The content of MDA is gradually decreased with the increase of soil Cd concentration, and integral level is lower than control group;MDA content is in Cd There is 0.33 ± 0.005 μm of ol/g of minimum value when being 100mg/kg in concentration for the treatment of, and year-on-year control group reduces 32.65%;In Cd Concentration for the treatment of be 400mg/kg when, content be 0.42 ± 0.005 μm of ol/, still lower than control group 18.37%.Daphne odera blade Interior Lipid peroxidation metabolism degree is lower, and the film rouge in blade is not affected by injury, and daphne odera has stronger tolerance to Cd;
4.2, influence of the Cadmium treated of various concentration to daphne odera fluorescent characteristic:
When soil Cd concentration is 25mg/kg, daphne odera appearance maximum Fv/Fm value, 0.87 ± 0.02, it is higher than control group 1.16%;Minimum value appear in Cd concentration be 400mg/kg when, lower than control group 4.65%.The Fv/Fm value of daphne odera between Between 0.82-0.87, meet the normal range (NR) of general plant.This explanation, daphne odera is under Cd stress in its photosynthetic organs PSII is not affected by damage.
The NPQ value of daphne odera is gradually increasing with the raising of soil Cd concentration, and maximum value appears in Cd concentration for the treatment of and is When 400mg/kg, 0.45 ± 0.07, higher than control group by 80.00%, minimum value then appears in control group, and 0.25 ± 0.02.Seven In light protective capability in fragrant Photosynthetic, can enhance with the raising of soil Cd concentration, and photosynthetic organs are not affected by damage, plant Object can be normally carried out photosynthesis.
There is maximum value under the Cd stress of 25mg/kg in the Φ PSII value of daphne odera, higher than control group by 1.0%, remaining side of body Difference that there are no significant under compeling, daphne odera is under Cd stress, and intracorporal smooth protective capability enhancing, photosynthetic organs are not by light Stress, each photosynthetic process are not affected by influence, and photosynthesis can be normally carried out, and also be not affected by shadow to the fixation and assimilative capacicy of carbon It rings;
4.3, heavy metal Cd is in the intracorporal distribution of daphne odera and enrichment characteristics:
With the raising of heavy metal Cd concentration, the root of daphne odera, stem, also conspicuousness rises the Cd content being enriched in leaf therewith, Its different parts is different to the accumulation characteristic of Cd, when soil Cd level is between 0-50mg/kg, aerial part (stem+leaf) enrichment Cd ability be higher than subterraneous root;When soil Cd level is higher than 100mg/kg, subterraneous root is enriched with Cd speed and is higher than aerial part, With the increase of soil Cd concentration, the Cd content of daphne odera aerial part and under ground portion enrichment is continuously increased;The ground of daphne odera It is respectively 77.92 ± 1.20mg/kg that the Cd content of upper part and root enrichment, which has maximum value in the Cd stress of 400mg/kg, With 111.63 ± 6.94mg/kg, the Cd in environment can be constantly absorbed into the internal of plant by daphne odera, and with soil Cd concentration Increase and is continuously improved;
For soil Cd concentration in 0-50mg/kg, daphne odera is greater than 1 (1.19 ± 0.18-1.91 to the transhipment coefficient (TF) of Cd ±0.25);With the increase of soil Cd concentration, especially when soil Cd level is higher than 100mg/kg, daphne odera turns Cd Transporting coefficient, there was no significant difference less than 1 (0.7 ± 0.14-0.74 ± 0.08), and between various concentration processing;This illustrates that daphne odera can The heavy metal Cd of effective transfer root enrichment, aerial part bio-concentration factor and root bio-concentration factor are in 25mg/kg soil Maximum value 1.58 ± 0.04 and 1.38 ± 0.21 is respectively provided with when earth Cd, but significant with the raising of heavy metal Cd concentration for the treatment of It reduces, illustrates daphne odera under Cd stress, can constantly extract the heavy metal Cd in soil, but it extracts ability with soil Cd water Flat raising constantly reduces, and has maximum extracting ability when soil Cd concentration is 25mg/kg;;
5, discussion of results
5.1, under the stress of heavy metal Cd daphne odera leaf antioxidase response and protection mechanism:
When plant is coerced by arid, high temperature, low temperature and heavy metal etc., a large amount of active oxygen can generate in vivo, no Secondary stress is generated to plant after disconnected accumulation, makes the Lipid peroxidation metabolism of cell membrane, damages the cell membrane of plant;Antioxidant Enzymes System, be one of plant defense system, wherein SOD enzyme is the first barrier of Antioxidant Enzyme Systems, it by catalysis super oxygen yin from Sub- free radical O2 ?It is converted into H202With the reaction of ground state oxygen, a large amount of superoxide anion is removed, cell is avoided to come to harm, super oxygen Anion is converted into H202After ground state oxygen, the H of generation202It also can be to cell damage.POD enzyme and CAT enzyme can be by H202It urges Change is decomposed into water and oxygen, protects plant cell, and when plant is in stress or organ senescence, cell death, antioxidase is removed The rate of active oxygen can cause the Lipid peroxidation metabolism degree of cell membrane to enhance, final product malonaldehyde lower than the rate that it is generated Content also rise with it, therefore, the height of MDA content can reflect the Lipid peroxidation metabolism degree of cell.In this study, in seven Fragrant SOD enzyme activity in vivo and CAT enzyme activity do not occur significantly improving with the increase of Cd concentration, and POD enzyme activity is then with Fig. 3's Concentration increase first rises to be declined afterwards, this is similar to the experimental result on current beans seed in office;Moreover, MDA in daphne odera leaf Content is integrally lower than control group, illustrates under Cd stress, and cell membrane is not affected by injury, and antioxidase can be effectively protected seven In spiceleaf piece injured from Lipid peroxidation metabolism, daphne odera has very strong tolerance to heavy metal Cd;
5.2, under the stress of heavy metal Cd daphne odera chlorophyll fluorescence variation:
In plant chlorophyll fluorescence kinetics, the situation of change of every chlorophyll fluorescence parameters index can reflect and take the post as On influence photosynthetic in plant, Fv/Fm value reflects the degree of impairment of plant PS II for what adverse circumstance, the non-stress the case where Under, which not will receive the influence of species and growth conditions, be generally stabilized between 0.80-0.85, and therefore, which can also be anti- Mirror whether plant is forced, NPQ value is non-photochemistry fluorescent quenching coefficient, and the size of value reflects PSII reaction center Antenna beam consume excessive energy by improving non-radiation type heat dissipation after absorbing excessive luminous energy, protect photosynthetic The ability of mechanism damage is strong and weak, belongs to a kind of self-protective mechanism of plant, when plant is forced, non-photochemistry is glimmering Optical quenching coefficient NPQ, that is, plant light protective capability will appear variation, and value is bigger, and the light protective capability for indicating plant is stronger, phase The practical Photochemical Efficiency Φ PSII value of the PSII answered can be also varied, and Φ PSII indicates the practical Photochemical Efficiency of PSII, value Size represent the power of plant assimilating power, be worth bigger, the assimilatory power of plant is bigger, and the fixation and assimilative capacicy to carbon are also got over By force, in this study, the value of Fv/Fm and Φ PSII first rises and declines afterwards with the rising of cadmium concentration, the value of NPQ then constantly on Rise, this at present research annual fleabane herb various concentration Cd stress under the result of Chlorophyll Fluorescence it is similar, illustrate in seven For perfume (or spice) under Cd stress, intracorporal optical protection mechanism preferably protects photosynthetic organs, can carry out normal photosynthetic work With being not affected by the stress of cadmium;
5.3, heavy metal Cd coerces enrichment and the transfer characteristic of lower daphne odera:
Plant refers in the Heavy-metal Polluted Environment of high concentration that plant remains to normal growth to the patience of heavy metal, and It is not affected by apparent damage, and has a certain amount of heavy metal in vivo;Super enriching plant refers to that plant can utilize itself all kinds of mechanism, Heavy metal excess in environment is absorbed and is transported to aboveground vegetation part, and different heavy metals, to super enriching plant Definition is also different, and cadmium enriching plant refers to that the aerial part cadmium content of plant has to be larger than 100mg/kg, and transhipment coefficient reflects Transhipment complexity of certain element from plant root to aboveground vegetation part, bio-concentration factor then reflect it to heavy metal Accumulation ability power, in this study, daphne odera under the processing of each cadmium concentration, can normal growth, and and control group Without obvious morphological differences;After measured, intracorporal cadmium content is not up to the standard of Cd-hyperaccumulator, is not belonging to the plant of cadmium super enrichment Object, but stronger tolerance and enrichment transfer ability are shown to cadmium;
6, research conclusion
In this study, the daphne odera under Cd stress does not occur death and is poisoned phenomenon, shows stronger vitality, Intracorporal antioxidase is induced to protect plant cell not coerced to eliminate destruction of the active oxygen generated to cell membrane;Respectively Item chlorophyll fluorescence parameters also reflect daphne odera and are not affected by the larger stress of cadmium, can be normally carried out photosynthesis;To seven In fragrant intracorporal cadmium content have certain Cd accumulation amount in root, stem and leaf when being measured, but do not reach Cd-hyperaccumulator Standard, be not belonging to Cd-hyperaccumulator, daphne odera described above under the stress of cadmium, can normal growth, in vivo it is anti-oxidant The normal Scavenger of ROS of enzyme energy, photosynthesis are not affected by influence, have certain enrichment to cadmium and have stronger tolerance.
After adopting the above method, the invention has the following beneficial effects: a kind of heavy metal cadmium stress of the present invention is to daphne odera The research that characteristic influences, obtains the daphne odera under Cd stress and does not occur death and be poisoned phenomenon, show stronger vitality, Intracorporal antioxidase is induced to protect plant cell not coerced to eliminate destruction of the active oxygen generated to cell membrane;Respectively Item chlorophyll fluorescence parameters also reflect daphne odera and are not affected by the larger stress of cadmium, can be normally carried out photosynthesis;To seven In fragrant intracorporal cadmium content have certain Cd accumulation amount in root, stem and leaf when being measured, but do not reach Cd-hyperaccumulator Standard, be not belonging to Cd-hyperaccumulator, daphne odera described above under the stress of cadmium, can normal growth, in vivo it is anti-oxidant The normal Scavenger of ROS of enzyme energy, photosynthesis are not affected by influence, have certain extracting accumulation ability to cadmium in soil and have Stronger tolerance.
The above is only used to illustrate the technical scheme of the present invention and not to limit it, and those of ordinary skill in the art are to this hair The other modifications or equivalent replacement that bright technical solution is made, as long as it does not depart from the spirit and scope of the technical scheme of the present invention, It is intended to be within the scope of the claims of the invention.

Claims (1)

1. a kind of heavy metal cadmium coerces the research influenced on daphne odera characteristic, it is characterised in that: its research method is as follows:
(1), the preparation of experimental material
(1.1), vegetable material is annual daphne odera seedling;
It (1.2), is the red soil for not cultivating crop for examination soil;
(1.3), agents useful for same be cadmium nitrate, analysis it is pure;
(2), test method
(2.1), soil potted plant experiment: taking appropriate soil, after natural air drying, hammer are broken, with Cd2+Solution is uniformly mixed and distinguishes It is fitted into bag, every part of 10kg, Cd is set2+Concentration gradient be 0 (CK), 25,50,100,200,400mg/kg, using be not added Cd as Control, 5 repetitions of each processing, cultivating bag bottom entangled with polybag, is balanced 14 days, after balance period, selection plant height is close, Stem thickness is close, daphne odera seedling similar in leaf blade size and quantity and is transplanted in experiment basin, after plantation three months, carries out correlation and refers to Target measurement, during soil is balanced and planted, it is ensured that the water content of soil is 60% or so;
(2.2), the measurement of physical signs: the vitality test of superoxide dismutase uses nitroblue tetrazolium colorimetric method, catalase The measurement of vigor is measured using ultraviolet absorption method, the measurement of peroxidase activity is measured using guaiacol method, The measurement of mda content is measured using thiobarbituricacidα- method;
(2.3), the measurement of photosynthetic parameters the measurement of chlorophyll fluorescence parameters: is carried out using the portable photosynthetic instrument of Li-6400;Fine It evening 21:00-22:00, when measurement, use leaf chamber size for 3 × 2cm2, light source used, temperature, humidity, carbon dioxide are dense Degree is that under natural conditions, location parameter is initial fluorescence, maximum fluorescence, steady state fluorescence, fluorescence rises to can change thylakoid most Big fluorescence, and II maximal photochemistry efficiency of PS, non-photochemistry fluorescent quenching coefficient, the practical Photochemical Efficiency of PS II are calculated, it calculates Formula is as follows:
II maximal photochemistry efficiency of PS: Fv/Fm=(Fm-Fo)/Fm
Non- photochemistry fluorescent quenching coefficient: NPQ=(Fm-Fm')/Fm'
The practical Photochemical Efficiency of PS II: Φ PSII=(Fm'-Fs)/Fm', wherein F0 is initial fluorescence, Fm is maximum fluorescence, Fs For steady state fluorescence, Fm ' be fluorescence rise to can change thylakoid maximum fluorescence, Fv/Fm is II maximal photochemistry efficiency of PS, NPQ is Non- photochemistry fluorescent quenching coefficient, Φ PSII are the practical Photochemical Efficiency of PS II;
(2.4), the measurement of heavy metal cadmium content: after plantation three months, after the root, stem, leaf sample after weighing 0.2g drying respectively, It crushes, the sieving of 100 mesh, 8ml digestion solution is added, the concentration of digestion solution is HNO3∶H2O2=6: 2, it is placed in microwave dissolver and carries out Resolution;It clears up and is cooled to room temperature completely to material, dilute HNO is added3After constant volume, planted using Flame Atomic Absorption Spectrometry Determination Cd content in object material, replication 3 times, and calculate TF, that is, transhipment coefficient and and BCF, that is, concentration coefficient:
Transhipment coefficient=aerial part cadmium content/root that is averaged is averaged cadmium content
Root bio-concentration factor=root is averaged the content of cadmium in cadmium content/soil
Aerial part bio-concentration factor=aerial part is averaged the content of cadmium in cadmium content/soil;
(3), data processing
Data processing is carried out using Origin 8.5 and Past 2.08;
(4), interpretation of result
(4.1), influence of the various concentration Cd processing to the vigor and mda content of daphne odera antioxidase:
Under the stress of Cd, peak occur when the intracorporal SOD vigor of daphne odera is under 100mg/kg soil Cd stress is Difference that there are no significant under 425.15 ± 2.41U/g, remaining Cd stress, and substantially less than control group;The energy value of POD exists Maximum value occurs in 25mg/kg soil Cd when coercing be 137.24 ± 1.37U/ (gmin), and year-on-year control group increases 38.96%, minimum value occurs in soil Cd level when being 400mg/kg be 43.91 ± 1.61U/ (gmin), year-on-year control group drop Low 55.54%;There is 0.87 ± 0.03U/ of maximum value (gmin) when being 100mg/kg in the vigor soil Cd of CAT, compares on year-on-year basis Group increases 19.18%, difference that there are no significant under remaining Cd stress;SOD, POD, CAT 400mg/kg soil Cd stress under, Vigor is below control group, and year-on-year control group has dropped 16.75%, 55.54%, 5.48% respectively, and daphne odera is at Cd stress In reason, its active oxygen metabolism of vigor energy normal regulating balance of internal each antioxidase, protection plant preserves from, has to Cd There is stronger tolerance;
The content of MDA is gradually decreased with the increase of soil Cd concentration, and integral level is lower than control group;MDA content is in Cd processing There is 0.33 ± 0.005 μm of ol/g of minimum value when being 100mg/kg in concentration, and year-on-year control group reduces 32.65%;In Cd processing When concentration is 400mg/kg, content is 0.42 ± 0.005 μm of ol/, still lower than control group 18.37%, in daphne odera blade Lipid peroxidation metabolism degree is lower, and the film rouge in blade is not affected by injury, and daphne odera has stronger tolerance to Cd;
(4.2), influence of the Cadmium treated of various concentration to daphne odera fluorescent characteristic:
When soil Cd concentration is 25mg/kg, daphne odera appearance maximum Fv/Fm value, 0.87 ± 0.02, it is higher than control group 1.16%;Minimum value appear in Cd concentration be 400mg/kg when, lower than control group 4.65%;The Fv/Fm value of daphne odera between Between 0.82-0.87, meet the normal range (NR) of general plant, this explanation, daphne odera is under Cd stress in its photosynthetic organs PSII is not affected by damage;
The NPQ value of daphne odera is gradually increasing with the raising of soil Cd concentration, and it is 400mg/ that maximum value, which appears in Cd concentration for the treatment of, When kg, 0.45 ± 0.07, higher than control group by 80.00%, minimum value then appears in control group, and 0.25 ± 0.02, daphne odera light The light protective capability in mechanism is closed, can be enhanced with the raising of soil Cd concentration, and photosynthetic organs are not affected by damage, plant can be just Often carry out photosynthesis;
There is maximum value under the Cd stress of 25mg/kg in the Φ PSII value of daphne odera, higher than control group by 1.0%, under remaining stress Difference that there are no significant, daphne odera under Cd stress, do not coerced by light by intracorporal smooth protective capability enhancing, photosynthetic organs Compel, each photosynthetic process is not affected by influence, and photosynthesis can be normally carried out, and is also not affected by shadow to the fixation and assimilative capacicy of carbon It rings;
(4.3), heavy metal Cd is in the intracorporal distribution of daphne odera and enrichment characteristics:
With the raising of heavy metal Cd concentration, the root of daphne odera, stem, also conspicuousness rises the Cd content being enriched in leaf therewith, no Different with accumulation characteristic of the position to Cd, when soil Cd level is between 0-50mg/kg, the Cd ability of aerial part enrichment is higher than Subterraneous root;When soil Cd level is higher than 100mg/kg, subterraneous root is enriched with Cd speed and is higher than aerial part, with soil Cd concentration Increase, daphne odera aerial part and under ground portion enrichment Cd content be continuously increased;The aerial part of daphne odera and root The Cd content of enrichment 400mg/kg Cd stress when have maximum value be respectively 77.92 ± 1.20mg/kg and 111.63 ± 6.94mg/kg, the Cd in environment can be constantly absorbed into the internal of plant by daphne odera, and constantly be mentioned with the increase of soil Cd concentration It is high;
For soil Cd concentration in 0-50mg/kg, daphne odera is 1.19 ± 0.18-1.91 ± 0.25 to the transhipment coefficient of Cd;With The increase of soil Cd concentration, especially when soil Cd level is higher than 100mg/kg, daphne odera to the transhipment coefficient of Cd be 0.7 ± 0.14-0.74 ± 0.08, and there was no significant difference between various concentration processing;This illustrates that daphne odera can effectively shift root enrichment Heavy metal Cd, aerial part bio-concentration factor and root bio-concentration factor are respectively provided with maximum in 25mg/kg soil Cd Value 1.58 ± 0.04 and 1.38 ± 0.21, but significantly reduced with the raising of heavy metal Cd concentration for the treatment of, illustrate that daphne odera exists Under Cd stress, the heavy metal Cd in soil can be constantly extracted, but its extracting ability is constantly reduced with the raising of soil Cd level, And there is maximum extracting ability when soil Cd concentration is 25mg/kg;
(5), discussion of results
(5.1), under the stress of heavy metal Cd daphne odera leaf antioxidase response and protection mechanism:
When plant is coerced by arid, high temperature, low temperature and heavy metal etc., a large amount of active oxygen can generate in vivo, constantly product Secondary stress is generated to plant after tired, makes the Lipid peroxidation metabolism of cell membrane, damages the cell membrane of plant;Antioxidant Enzyme Systems are One of plant defense system, wherein SOD enzyme is the first barrier of Antioxidant Enzyme Systems, it is free by catalysis superoxide anion Base O2 ?It is converted into H202With the reaction of ground state oxygen, a large amount of superoxide anion is removed, cell is avoided to come to harm, superoxide anion It is converted into H202After ground state oxygen, the H of generation202It also can be to cell damage;POD enzyme and CAT enzyme can be by H202Catalytic decomposition For water and oxygen, plant cell is protected, when plant is in stress or organ senescence, cell death, antioxidase Scavenger of ROS Rate can lower than its generate rate, cause the Lipid peroxidation metabolism degree of cell membrane to enhance, the content of final product malonaldehyde Also it rises with it, therefore, the height of MDA content can reflect the Lipid peroxidation metabolism degree of cell, in this study, in daphne odera body SOD enzyme activity and CAT enzyme activity do not occur significantly improving with the increase of Cd concentration, and POD enzyme activity then increases with Cd concentration First rise and decline afterwards, this is similar to the experimental result on current beans seed in office;Moreover, the content of MDA is whole in daphne odera leaf Lower than control group, illustrate under Cd stress, cell membrane is not affected by injury, and daphne odera blade can be effectively protected in antioxidase It is injured from Lipid peroxidation metabolism, daphne odera has very strong tolerance to heavy metal Cd;
(5.2), under the stress of heavy metal Cd daphne odera chlorophyll fluorescence variation:
In plant chlorophyll fluorescence kinetics, the situation of change of every chlorophyll fluorescence parameters index be can reflect out any inverse On influence photosynthetic in plant, Fv/Fm value reflects the degree of impairment of plant PS II in border, in the case where non-stress, The value not will receive the influence of species and growth conditions, be generally stabilized between 0.80-0.85, and therefore, which also can reflect Whether plant is forced out, and NPQ value is non-photochemistry fluorescent quenching coefficient, and the size of value reflects PSII reaction center Antenna beam consumes excessive energy, protects photosynthetic machine by improving non-radiation type heat dissipation after absorbing excessive luminous energy The ability of structure damage is strong and weak, belongs to a kind of self-protective mechanism of plant, when plant is forced, non-photochemistry fluorescence The light protective capability that the i.e. plant of coefficient NPQ is quenched will appear variation, and value is bigger, and the light protective capability for indicating plant is stronger, accordingly The practical Photochemical Efficiency Φ PSII value of PSII can also be varied, Φ PSII indicate the practical Photochemical Efficiency of PSII, value Size represents the power of plant assimilating power, and value is bigger, and the assimilatory power of plant is bigger, also stronger to the fixation and assimilative capacicy of carbon, In this study, the value of Fv/Fm and Φ PSII first rises and declines afterwards with the rising of cadmium concentration, and the value of NPQ then constantly rises, this To at present research annual fleabane herb various concentration Cd stress under the result of Chlorophyll Fluorescence it is similar, illustrate daphne odera in cadmium Under stress, intracorporal optical protection mechanism preferably protects photosynthetic organs, can carry out normal photosynthesis, not by To the stress of cadmium;
(5.3), heavy metal Cd coerces enrichment and the transfer characteristic of lower daphne odera:
Plant refers in the Heavy-metal Polluted Environment of high concentration that plant remains to normal growth to the patience of heavy metal, not by To apparent damage, and there is a certain amount of heavy metal in vivo;Super enriching plant refers to that plant can be using itself all kinds of mechanism, by ring Heavy metal excess in border absorbs and is transported to aboveground vegetation part, and different heavy metals, the definition to super enriching plant Also different, cadmium enriching plant refers to that the aerial part cadmium content of plant has to be larger than 100mg/kg, and transhipment coefficient reflects certain Transhipment complexity of the element from plant root to aboveground vegetation part, bio-concentration factor then reflect its richness to heavy metal The power of collection ability, in this study, daphne odera is under the processing of each cadmium concentration, equal energy normal growth, and with control group without bright Aobvious morphological differences;After measured, intracorporal cadmium content is not up to the standard of Cd-hyperaccumulator, is not belonging to Cd-hyperaccumulator, But stronger tolerance and enrichment transfer ability are shown to cadmium;
(6), research conclusion
In this study, the daphne odera under Cd stress does not occur death and is poisoned phenomenon, shows stronger vitality, in vivo Antioxidase be induced to protect plant cell not coerced to eliminate destruction of the active oxygen to cell membrane generated;Every leaf Green element fluorescence parameter also reflects daphne odera and is not affected by the larger stress of cadmium, can be normally carried out photosynthesis;To daphne odera There is certain Cd accumulation amount when intracorporal cadmium content is measured, in root, stem and leaf, but does not reach the mark of Cd-hyperaccumulator Standard is not belonging to Cd-hyperaccumulator, and daphne odera described above is under the stress of cadmium, energy normal growth, internal antioxidase energy Normal Scavenger of ROS, photosynthesis are not affected by influence, have certain enrichment to cadmium and have stronger tolerance.
CN201811137494.2A 2018-09-28 2018-09-28 A kind of research that heavy metal cadmium stress influences daphne odera characteristic Pending CN109121988A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201811137494.2A CN109121988A (en) 2018-09-28 2018-09-28 A kind of research that heavy metal cadmium stress influences daphne odera characteristic

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201811137494.2A CN109121988A (en) 2018-09-28 2018-09-28 A kind of research that heavy metal cadmium stress influences daphne odera characteristic

Publications (1)

Publication Number Publication Date
CN109121988A true CN109121988A (en) 2019-01-04

Family

ID=64813165

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201811137494.2A Pending CN109121988A (en) 2018-09-28 2018-09-28 A kind of research that heavy metal cadmium stress influences daphne odera characteristic

Country Status (1)

Country Link
CN (1) CN109121988A (en)

Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN110106194A (en) * 2019-04-26 2019-08-09 中国计量大学 The ORF segment of POD P7 gene and its application in raising plant cadmium stress tolerance, reduction Cd accumulation
CN110633921A (en) * 2019-10-11 2019-12-31 大连大学 Comprehensive evaluation method for soil-resistant high-pH-value capability of blueberry varieties
CN110706123A (en) * 2019-11-19 2020-01-17 大连大学 Screening method for identification index of higher soil pH value stress resistance of cowberry
CN110907438A (en) * 2019-10-24 2020-03-24 安徽建筑大学 Method for evaluating soil chromium pollution ecotoxicity based on pennisetum hydridum
CN112375564A (en) * 2020-11-12 2021-02-19 中山大学 Method for preparing environment-friendly optical material by utilizing rare earth hyper-enriched plants
CN115839937A (en) * 2022-12-20 2023-03-24 江苏省中国科学院植物研究所 Taxus chinensis stress detection method based on chlorophyll fluorescence imaging technology

Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102295692A (en) * 2011-08-26 2011-12-28 中国科学院华南植物园 Rice metal-tolerant protein OsMPT1 as well as encoding gene and RNA (Ribonucleic Acid) interference segment thereof
CN104698130A (en) * 2015-02-03 2015-06-10 上海交通大学 Method for appraising cadmium tolerance of chrysanthemums
CN104805020A (en) * 2015-05-08 2015-07-29 黑龙江大学 Arbuscular mycorrhiza fungus capable of improving saline-alkali tolerance of Elaeagnus angustifolia
CN108432562A (en) * 2018-02-24 2018-08-24 新宁县永鑫药材开发有限公司 The artificial cultivation and collecting method of macleaya cordata

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102295692A (en) * 2011-08-26 2011-12-28 中国科学院华南植物园 Rice metal-tolerant protein OsMPT1 as well as encoding gene and RNA (Ribonucleic Acid) interference segment thereof
CN104698130A (en) * 2015-02-03 2015-06-10 上海交通大学 Method for appraising cadmium tolerance of chrysanthemums
CN104805020A (en) * 2015-05-08 2015-07-29 黑龙江大学 Arbuscular mycorrhiza fungus capable of improving saline-alkali tolerance of Elaeagnus angustifolia
CN108432562A (en) * 2018-02-24 2018-08-24 新宁县永鑫药材开发有限公司 The artificial cultivation and collecting method of macleaya cordata

Non-Patent Citations (4)

* Cited by examiner, † Cited by third party
Title
杨永红等: "煤矸山周围土壤和乡土植物的重金属含量研究", 《安徽农业大学学报》 *
洪立洲等: "NaCl胁迫对马齿苋光合作用及叶绿素荧光特性的影响", 《西北植物学报》 *
胡仲义 李修鹏: "铅胁迫对全缘冬青幼苗生长与生理的影响", 《浙江林业科技》 *
赵斌等: "铬胁迫对美人蕉生理生态特性与铬积累的影响", 《科学技术与工程》 *

Cited By (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN110106194A (en) * 2019-04-26 2019-08-09 中国计量大学 The ORF segment of POD P7 gene and its application in raising plant cadmium stress tolerance, reduction Cd accumulation
CN110106194B (en) * 2019-04-26 2020-08-11 中国计量大学 ORF fragment of POD P7 gene and application thereof in improving cadmium stress tolerance and reducing cadmium accumulation of plants
CN110633921A (en) * 2019-10-11 2019-12-31 大连大学 Comprehensive evaluation method for soil-resistant high-pH-value capability of blueberry varieties
CN110907438A (en) * 2019-10-24 2020-03-24 安徽建筑大学 Method for evaluating soil chromium pollution ecotoxicity based on pennisetum hydridum
CN110706123A (en) * 2019-11-19 2020-01-17 大连大学 Screening method for identification index of higher soil pH value stress resistance of cowberry
CN112375564A (en) * 2020-11-12 2021-02-19 中山大学 Method for preparing environment-friendly optical material by utilizing rare earth hyper-enriched plants
CN112375564B (en) * 2020-11-12 2022-03-15 中山大学 Method for preparing environment-friendly optical material by utilizing rare earth hyper-enriched plants
CN115839937A (en) * 2022-12-20 2023-03-24 江苏省中国科学院植物研究所 Taxus chinensis stress detection method based on chlorophyll fluorescence imaging technology
CN115839937B (en) * 2022-12-20 2024-01-09 江苏省中国科学院植物研究所 Taxus chinensis stress detection method based on chlorophyll fluorescence imaging technology

Similar Documents

Publication Publication Date Title
CN109121988A (en) A kind of research that heavy metal cadmium stress influences daphne odera characteristic
Pang et al. Yield and photosynthetic characteristics of flag leaves in Chinese rice (Oryza sativa L.) varieties subjected to free-air release of ozone
Muradoglu et al. Cadmium toxicity affects chlorophyll a and b content, antioxidant enzyme activities and mineral nutrient accumulation in strawberry
Kataria et al. Intraspecific variations in growth, yield and photosynthesis of sorghum varieties to ambient UV (280–400 nm) radiation
Kareem et al. Zinc oxide nanoparticles interplay with physiological and biochemical attributes in terminal heat stress alleviation in mungbean (Vigna radiata L.)
Asemoloye et al. Mediational influence of spent mushroom compost on phytoremediation of black-oil hydrocarbon polluted soil and response of Megathyrsus maximus Jacq
Agrawal et al. Role of ethylene diurea (EDU) in assessing impact of ozone on Vigna radiata L. plants in a suburban area of Allahabad (India)
Berenbaum et al. Furanocoumarins in seeds of wild and cultivated parsnip
Gong et al. Gibberellic acid application on biomass, oxidative stress response, and photosynthesis in spinach (Spinacia oleracea L.) seedlings under copper stress
Chen et al. High correlation between thermotolerance and photosystem II activity in tall fescue
Sarieva et al. Adaptation potential of photosynthesis in wheat cultivars with a capability of leaf rolling under high temperature conditions
Yu et al. Stomatal and non-stomatal limitations to photosynthesis in field-grown grapevine cultivars
Jiao et al. Stomatal and non-stomatal factors regulated the photosynthesis of soybean seedlings in the present of exogenous bisphenol A
Hassena et al. Potential effects of arbuscular mycorrhizal fungi in mitigating the salinity of treated wastewater in young olive plants (Olea europaea L. cv. Chetoui)
Lu et al. Effect of NaCl-induced changes in growth, photosynthetic characteristics, water status and enzymatic antioxidant system of Calligonum caput-medusae seedlings
Cha-um et al. Physio-biochemical responses of oil palm (Elaeis guineensis Jacq.) seedlings to mannitol-and polyethylene glycol-induced iso-osmotic stresses
Yang et al. Heavy metal domestication enhances beneficial effects of arbuscular mycorrhizal fungi on lead (Pb) phytoremediation efficiency of Bidens parviflora through improving plant growth and root Pb accumulation
Chen et al. Effects of 60-day NO 2 fumigation on growth, oxidative stress and antioxidative response in Cinnamomum camphora seedlings
Huang et al. Photosynthesis performance and antioxidative enzymes response of Melia azedarach and Ligustrum lucidum plants under Pb–Zn mine tailing conditions
Mukarram et al. Suffer or survive: Decoding salt-sensitivity of lemongrass and its implication on essential oil productivity
Fu et al. Effects of high soil lead concentration on photosynthetic gas exchange and chlorophyll fluorescence in Brassica chinensis L.
Bidalia et al. Tolerance of Mitragyna parvifolia (Roxb.) Korth. seedlings to NaCl salinity
Qian et al. Effect of soil aeration treatment on the physiological and biochemical characteristics of Phyllostachys praecox under the organic material mulching
Tang et al. Heavy metal cadmium tolerance on the growth characteristics of industrial hemp (Cannabis sativa L.) in China
Wang et al. Effects of polyploidization on photosynthetic characteristics in three Lilium species

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
RJ01 Rejection of invention patent application after publication

Application publication date: 20190104

RJ01 Rejection of invention patent application after publication