CN101992207B - Heavy metal-polycyclic aromatic hydrocarbon combined pollution reinforcing repairing agent and application thereof - Google Patents

Heavy metal-polycyclic aromatic hydrocarbon combined pollution reinforcing repairing agent and application thereof Download PDF

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CN101992207B
CN101992207B CN200910013169XA CN200910013169A CN101992207B CN 101992207 B CN101992207 B CN 101992207B CN 200910013169X A CN200910013169X A CN 200910013169XA CN 200910013169 A CN200910013169 A CN 200910013169A CN 101992207 B CN101992207 B CN 101992207B
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soil
polycyclic aromatic
aromatic hydrocarbon
heavy metal
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魏树和
杨传杰
周启星
刘睿
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Institute of Applied Ecology of CAS
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Abstract

The invention relates to phytoremediation of environment pollution, in particular to a reinforcing repairing agent of a hyperaccumulator nightshade, which comprises the following components of glycine, glutamic acid and cysteine that have a mol ratio of 0.1-1.0:0.1-1.0:0.1-1.0. In cadmium-polycyclic aromatic hydrocarbon combined pollution pot culture soil in which the hyperaccumulator nightshade is transplanted, the glycine, the glutamic acid and the cysteine are mixed and poured in the soil in a form of a water mixture according to the content of 0.1-1.0mmol/kg every 15 days for 3 times; and when the hyperaccumulator nightshade grows up, the hyperaccumulator nightshade and the soil sample are harvested. Compared with the reinforcing repairing agent without being added with amino acid, low quantity of the mixture of the glycine, the glutamic acid and the cysteine has the best treatment effect, the Cd content of the upper part of the nightshade soil is increased by 2.26 times, and the removal rate of the total amount of polycyclic aromatic hydrocarbon in the soil reaches 34.5 percent, thus the repairing efficiency of the Cd and the polycyclic aromatic hydrocarbon by the nightshade are remarkably improved.

Description

One heavy metal species-polycyclic aromatic hydrocarbon combined contamination soil is strengthened renovation agent and application thereof
Technical field
The present invention relates to the phytoremediation technology of heavy metal-polycyclic aromatic hydrocarbon combined contamination soil, specifically a kind of reinforcement renovation agent of ultra enrichment repair plant black nightshade.
Background technology
Along with the variation of pollutant emission, complicated and frequentization; The contaminated degree of major receptors soil of pollutant increases the weight of day by day; Also outstanding all the more (the document 1:Paton GI of the rational characteristic of complexity that contaminated soil is repaired and refractory; Viventsova E, Kumpene J, et al.2006.An ecotoxicityassessment of contaminated forest soils from the Kola Peninsula.Science ofthe Total Environment; 355 (13): 106-117); Wherein heavy metal-organic combined pollution is more common pollution type, like Cd-polycyclic aromatic hydrocarbon (Polycyclic aromatic hydrocarbons, PAHs) combined pollution.Cadmium can suppress the plant growth, plant is produced toxic action (document 2:Schill RO when low concentration through reducing approach such as photosynthesis of plant, generation oxidative stress;
Figure G200910013169XD00011
H;
Figure G200910013169XD00012
HR.2003.Laboratory simulation of a mining accident:acutetoxicity hsc/hsp 70response and recovery from sress in Gammarus fossarum (Crustacea smphipoda) exposed to a pulse of cadmium.Biometals; 16:391-401); And to some extent humans and animals is produced toxic action, also can bring out canceration; And PAHs is one type of persistence organic pollutant, and biology is had chronic toxicity and carcinogenic, teratogenesis, mutagenicity.Because Cd, PAHs shows as in soil environment has disguise and chronicity, causes the difficulty of repairing this type of combined contamination soil to strengthen, seeking efficient, safe, economic recovery technique becomes the realistic problem of needing solution badly.Phytoremediation technology have physics, chemical repair method incomparable cost, to be difficult for causing secondary pollution, to beautify the environment, be easy to be advantages such as society is accepted; Become recovery technique (the document 3:Chaney RL that has development potentiality; Malik M; Li YM.1997.Phytoremediation of soil metals.Current Opinions in Biotechnology, 8:279-284; Brooks RR, Chambers MF, Nickls L J, et al.1998.Phytomining.Trends in Plant Science, 3 (9): 359-362).The phytoremediation of heavy-metal contaminated soil mainly is to remove through the excess of super enriching plant or enriching plant to be used for realizing (document 4: Wei Shuhe; Zhou Qixing; Pavel V.Koval; Galina A.Belogolova. organic contamination environment phytoremediation technology. ecological magazine .2006,25 (6): 716-721); For organic contamination such as polycyclic aromatic hydrocarbon mainly is to utilize the degradation of plant rhizosphere circle microorganism to accomplish (document 4: Wei Shuhe; Zhou Qixing; Pavel V.Koval, Galina A.Belogolova. organic contamination environment phytoremediation technology. ecological magazine .2006,25 (6): 716-721).But it is restricted with some that phytoremediation technology also exists some defectives, and the own biological characteristics of environmental condition and plant influences as very easily receiving, repairing efficiency is long etc.So need to adopt some to strengthen the efficient that reclamation activities improves phytoremediation, in the hope of reference being provided for improving early of this technology.
Coerce down in heavy metal pollution; A lot of plants have formed the harm that certain self-protective mechanism is resisted heavy metal ion; Like a series of little molecules (citrate, glutathione, plant complexing element etc.) of biosynthesis with complexation heavy metal ion ability; Form the lower compound of toxicity with free heavy metal ion complexing, and it is stored in the vacuole of plant cell.Wherein plant complexing element is a detoxifcation material important in the plant. plant complexing element is the one type of sulfydryl chelating polypeptide that produces in the cytoplasm liquid under the stress-inducings such as heavy metal such as Ni, Cd, Zn, Te, Au, Hg, Pb, As, Se; Wherein Cd is the strongest interior inducible factor of body; And the performance inducing action be metal ion free in the cytoplasm (document 5:Rauser WE.1995.Phytochelatins and related peptides.Plant Physiology, 109:1141-1149).PCs (Phytochelatins) is one type of polypeptide that is rich in cysteine (cysteine), is that original substrate generates through a series of enzymatic reactions by cysteine, glutamic acid, glycine.Cys sulfydryl among the PCs can with the cd in the born of the same parents 2+Form coordinate bond; And then formation PCs-Cd compound; The toxicity of this compound pair cell greatly reduces, and plant has also further taked vacuole compartmentation (compartmentation) that compound is fixed in the vacuole in addition, has further reduced the toxic action of Cd to plant.But under Cd-PAHs combined pollution condition, the original substrate of external source PCs absorbs black nightshade and the characteristic of accumulation Cd and to the influence of degrading polycyclic aromatic hydrocarbons effect in the soil, does not also appear in the newspapers, and this also is the problem that phytoremediation technology presses for solution.
Summary of the invention
The object of the present invention is to provide a kind of result of use heavy metal-polycyclic aromatic hydrocarbon combined contamination soil good, that can improve the crop remediation efficiency to strengthen renovation agent and application thereof.
For realizing above-mentioned purpose, the technical scheme that the present invention adopts is:
One heavy metal species-polycyclic aromatic hydrocarbon combined contamination soil is strengthened renovation agent, and its composition is calculated in molar ratio as, glycine: glutamic acid: cysteine=0.1-1.0: 0.1-1.0: 0.1-1.0.
Said reinforcement renovation agent can add in kind and be implanted with in the heavy metal-polycyclic aromatic hydrocarbon combined contamination soil of super enriching plant and/or enriching plant, to improve super enriching plant (black nightshade) and/or the enriching plant remediation efficiency to heavy metal such as cadmium and polycyclic aromatic hydrocarbon.
Said reinforcement renovation agent glycine, glutamic acid or the cysteine concentration that adds in contaminated soil is respectively 0.1-1.0mmol/kg soil, preferably is respectively 0.2-0.6mmol/kg soil.
On the soil of land for growing field crops or Polluted area, when directly applying the present invention and strengthening renovation agent, strengthen the every kg soil that adds in concentration adopted of renovation agent in contaminated soil, it is with the soil weight metering of the 0-20 centimetre of dark soil thickness in soil layer surface.
. the content 0.3-100mg/kg of heavy metal Cd in the said contaminated soil, the content 0.3-600mg/kg of polycyclic aromatic hydrocarbon PAHs; Said super enriching plant is a black nightshade.
The present invention mixes with the form of water mixed liquid by the content of 0.1-1.0mmol/kg on the contaminated soil of plantation black nightshade and pours into glycine, glutamic acid and cysteine; When treating that black nightshade is ripe; Results plant and soil-like are compared with not adding amino acid whose contrast, and the glycine of low dosage, glutamic acid and cysteine mixed liquor treatment effect are best; Black nightshade overground part Cd content has increased by 2.26 times; Simultaneously, the clearance of soil polycyclic aromatic hydrocarbon total amount can reach 39.3%, has improved the remediation efficiency of black nightshade to cadmium and polycyclic aromatic hydrocarbon significantly.
Description of drawings
Fig. 1 exogenous amino acid is to the influence of black nightshade plant height;
Fig. 2 exogenous amino acid is to the influence of black nightshade overground part dry weight.
The specific embodiment
The embodiment exogenous amino acid is to the reinforcement repair of heavy metal-polycyclic aromatic hydrocarbon combined pollution vegetable field soil
1 test material
The combined pollution vegetable field soil picks up from the Shen of Shenyang City's Dongling District and comforts the irrigated area, the vegetables field of irrigating for many years for petroleum waste water (be the paddy field in the past, and before 10 years, changed the vegetables field into).Soil types is a yellowish soil, and its physicochemical property is a pH value 6.9, organic 17.95mgkg -1, full N 1.32mgkg -1, full P 1.39mgkg -1, quick-acting K 144.36mgkg -1The total cadmium content 0.711mgkg of soil -1, 2 grade standards above national soil environment quality GB15618-1995 belong to the cadmium pollution horticultural vegetable field soil; 16 kinds of polycyclic aromatic hydrocarbon total amounts are 0.569mgkg in the soil -1, 2-4 ring polycyclic aromatic hydrocarbon content is 0.462mgkg -1, 5-6 ring polycyclic aromatic hydrocarbon content is 0.106mgkg -1, benzo (a) pyrene content is 0.026mgkg -1, to compare with Dutch soil remediation desired value, polycyclic aromatic hydrocarbon content obviously exceeds standard in institute's collection soil.
Rehabilitation plant is black nightshade (Solanum nigrum), and seed picks up from the non-dirty agricultural soil of irritating in ecological experiment station, Chinese Academy of Sciences Shenyang.
2 test methods
According to synthetic level of PCs in the plant and the effect in the detoxification processes in plant thereof; Experimental design cysteine (Cys), glycine (Gly), the single processing of glutamic acid (Glu); And glycine (Gly)+glutamic acid (Glu), glycine (Gly)+glutamic acid (Glu)+cysteine (Cys) Combined Processing, pour into the form of water mixed liquid, adding concentration range is 0.1-1.0mmol/kg; Be divided into two levels of low dosage 0.3mmol/kg and high dose 0.9mmol/kg, specifically see table 1.Other establishes 1 and does not add amino acid whose contrast, totally 11 processing, and every processing repetition 3 times (pouring into altogether 3 times) adopts liquid to add method, divides to add for three times, and interval of adding is 15 days.
Test is carried out in the greenhouse.To supply the air-dry back of examination soil to cross the 4mm sieve, accurately the weighing 1kg soil plastic tub of packing into; Black nightshade seed is seeded in Miao Panzhong; When treating that the black nightshade seedling grows to 3-5 sheet spire; Select the consistent black nightshade seedling of growth to move into respectively and respectively handles in the basin, every potted plant 2 seedling. control the temperature 25-30 of culturing room ℃, air humidity 50%-80%, intensity of illumination 350-450umol/m 2S, light application time 08:00-17:30.Transplant after 15 days, when treating that seedling grows to the 10cm left and right sides, corresponding each processing adds respectively, and irregularly waters running water according to basin lack of water situation, makes soil moisture content often remain on about 80% of field capacity.For preventing the filter loss of treatment fluid leaching, also in time effusion is refunded in the basin at basin held plastic pallet.After 80 days in plant maturity sampling (when treating that promptly black nightshade is ripe, results plant and soil-like).
Table 1 cysteine, glycine, glutamic acid processing horizontal table (mmol/kg)
3 sample analysis
The plant sample part of results is used for the mensuration of overground part content of beary metal, and remainder root division, stem, leaf, fruit 4 parts are fully washed with running water respectively; And then use deionized water rinsing; The drop branch that anhydrates, the 30min that under 105 ℃, completes dries to constant weight in baking oven under 70 ℃ then.Plant sample crushing screening after the oven dry is subsequent use, and it is subsequent use that 100 mesh sieves are crossed in the air-dry back of pedotheque.Plant reaches upward, and the earth sample all adopts HNO 3-HClO 4Method digestion (the two volume ratio is 3: 1), the atomic absorption spectrophotometer method is measured the content of Cd, and atomic absorption spectrophotometer is the 180-80 of Hitachi, and the absorbing wavelength of cadmium is 228.8.The mensuration of basic physical and chemical such as the content of organic matter of soil adopts conventional assay method.
100 mesh sieves are crossed in the air-dry back of the pedotheque of results, are stored in-80 ℃ of refrigerators subsequent use.P in soil AHs method for distilling is with reference to Song Yufang (1995) and Gao Yanzheng (2005).Take by weighing the 5.0g pedotheque in 25ml glass centrifuge tube,, adopt the mode of changing water to control therebetween and extract temperature below 40 ℃, with 4000rmin with the carrene ultrasonic extraction 2h of 15ml -1Centrifugalize and draw supernatant and in Rotary Evaporators, evaporate near doing, add the cyclohexane dissolving of 1.00ml again, accurately draw 0.5ml and cross the purification of 1g silicagel column, with n-hexane-carrene (volume ratio is 1: 1) mixed liquor wash-out of 11ml.Begin behind the 1ml eluent before discarding to collect, with the eluent of collecting in 40 ℃ of constant temperature down rotation be evaporated to driedly, again with the acetonitrile dissolving and be settled to 1ml, cross and go up machine behind the 0.45 μ m organic facies filter membrane and measure.
The mensuration of PAHs adopts fluorescence-ultraviolet series connection detection-high performance liquid chromatography (Rao Zhu etc., 2007).HPLC is Waters 1525; Fluorescence detector (Multi λ Fluorescence Detector) is Waters 2475; UV-detector (Dual λ Absorbance Detector) is Waters2487, chromatographic column be the polycyclic aromatic hydrocarbon chromatographic column specially (4.6 * 250mm, 5um).Analysis condition: with the acetonitrile/water is that (0-3min acetonitrile/water volume ratio is 60: 40 to eluent gradient drip washing 36min; 3-30min acetonitrile/water volume ratio is 100: 0; 30-36min acetonitrile/water volume ratio is 60: 40).Flow velocity 1.00mlmin -1, sample size is 20ul, 25 ℃ of column temperatures, and the corresponding mensuration wavelength of 16 kinds of PAHs is referring to (2007) such as Rao Zhu.With 16PAHs mixing standard specimen is external standard, directly contrasts with retention time and peak area and carries out the qualitative and quantitative of PAHs.This method is linear better to the mensuration of 16 kinds of PAHs, and the correlation coefficient r value is all greater than 0.999, and the scope of detecting is 0.011-0.513ng, to the recovery of standard addition of 16 kinds of PAHs except that the naphthalene of 2 rings be 53.4% all the other all between 75%-110%.
4 data statistics
The data that obtain are carried out statistical analysis with Microsoft Excel and SPSS16.0, utilize the new multipole difference check of Duncan to carry out significance test of difference (p<0.05).
5 results
5.1 exogenous amino acid is to the influence of black nightshade growth characteristics
Fig. 1, Fig. 2 have provided black nightshade plant height and the upperground part biomass situation of change under the indoor pot condition respectively.From seeing in appearance, under Cd-PAHs combined pollution condition, minus green, the symptom of being coerced such as withered and yellow do not appear in black nightshade normal growth, blade.Obviously, heavy metal and polycyclic aromatic hydrocarbon do not produce inhibitory action to the normal growth of plant under this experiment condition.Plant plant height and overground part dry weight show as corresponding to rule to the reaction of additive.Do not compare with adding amino acid whose contrast, single factor of cysteine (Cys), glycine (Gly), each concentration level of glutamic acid (Glu) is handled does not have appreciable impact (p<0.05) to plant plant height and overground part dry weight; And each Combined Processing all has significant facilitation (p<0.05) to it.
5.2 exogenous amino acid is to absorbing the influence of Cd in the black nightshade body
Table 2 has provided different aminoacids and has handled black nightshade root, stem, leaf, fruit and 5 portion C d of overground part content down.Can be found out that by table 2 each is handled, and Cd content conspicuousness increases outer (p<0.05) in the disleaf, the content increase of root, stem, fruit and overground part all reaches utmost point significance (p<0.01).The cumulant of plant shoot Cd still shows stronger extraction and accumulation ability greater than its cumulant at underground part under low concentration Cd pollutional condition, and different aminoacids handles and can significantly strengthen black nightshade Cd is extracted and accumulation ability, as handling 0.3mmolkg -1Gly+0.3mmolkg -1Glu+0.3mmolkg -1Cys makes the comparison of black nightshade overground part Cd content according to having increased by 2.26 times.On the whole; The facilitation that the complex factors of variable concentrations level are handled the plant absorbing heavy metal is superior to single factor processing; And 3 factor treatment effects are superior to 2 factors to be handled; Explain when adding the synthetic required whole amino acid of PCs and can improve its growing amount in plant, promoted the absorption of plant Cd.
Table 2 exogenous amino acid is to the influence of Cd accumulation in the black nightshade body
Figure G200910013169XD00061
Super enriching plant (Hyperaccumulator) is meant accumulation of ability excess or the plant that accumulates several heavy metal elements simultaneously, and possesses critical value content, transfer and enrichment characteristics, and its transfer and enrichment characteristics mainly characterize through transfer ratio and concentration coefficient.Transfer ratio (translocationfactor; TF) be meant the content of overground part element and the ratio of underground part constituent content of the same race; Being used for estimating the ability of plant transhipment heavy metal. transfer ratio is big more, and then heavy metal is strong more to overground part organ turn-over capacity from root.For super enriching plant, its overground part content of beary metal is greater than the root content of beary metal.Can find out that from table 3 under low concentration Cd-PAHs combined pollution condition, each handles TF>1, black nightshade still possesses stronger transfer ability to low concentration Cd.Concentration coefficient (bioaccumulationfactor; BF) also claim absorption coefficient, be meant the ratio of certain constituent content and elements in Soil content in the plant, characterize the complexity of migration of element in the soil-plant system; Concentration coefficient is high more, shows that plant shoot heavy metal accumulation mass fraction is big more.In soil, add the PCs substrate can the enhancement of plant overground part to the absorption of heavy metal, when adding low dosage 3 seed amino acid intermixtures, make the ability of plant absorbing heavy metal improve 2.26 times.The size of phytoremediation heavy metal ability and content and the upperground part biomass of plant heavy metal of body have direct relation, and (metal extractionratio MER) characterizes to use the heavy metal recovery rate usually.The heavy metal recovery rate is meant in amount and the soil of plant shoot accumulation heavy metal the ratio with the heavy metal species amount, promptly
MER=(C The overground part heavy metal* M The overground part dry weight/ C Heavy metal in soil* M Soil weight) * 100
Can know by table 3; Adding of the PCs substrate of variable concentrations level improved the recovery rate of black nightshade to low concentration cadmium in the soil to a great extent; Wherein cysteine is handled and is made the heavy metal recovery rate reach 1.80% and 1.83% respectively, compares with contrast and has improved 1.80 and 1.83 times respectively.In a word, under low concentration Cd-PAHs combined pollution condition, higher transfer ratio, concentration coefficient and heavy metal recovery rate are arranged all in the black nightshade body, demonstrate to Cd extract preferably, transfer and enrichment characteristics; Adding of PCs substrate can be strengthened the absorbability of black nightshade to Cd in the soil, quickens the removal speed of Cd in soil environment.
Table 3 exogenous amino acid is to the influence of concentration coefficient, transfer ratio and the heavy metal recovery rate of Cd
Figure G200910013169XD00062
5.3 exogenous amino acid is to the influence of PAHs degraded in the soil
Table 4 has provided the influence of amino acid to degrading polycyclic aromatic hydrocarbons effect in the soil.Can find out by table 4; Exogenous amino acid will be higher than the low-molecular-weight polycyclic aromatic hydrocarbon to the facilitation of polycyclic aromatic hydrocarbon with high molecular weight degraded in the soil; Its reason possibly be that exogenous amino acid is that edaphon provides common metabolism matrix, and metabolism is the biodegradable main mode of polycyclic aromatic hydrocarbon with high molecular weight altogether; In addition, along with the corresponding enhancing of degradation of the increase 5-6 ring polycyclic aromatic hydrocarbon and benzo (a) pyrene of glycine dosage, explain that glycine can provide the required C of common metabolism the source for the degraded of polycyclic aromatic hydrocarbon with high molecular weight.
Table 4 exogenous amino acid is to the enhancing degradation effect of PAHs in the soil
aNaphthalene, acenaphthene, acenaphthylene, fluorenes, anthracene, phenanthrene, fluoranthene, pyrene, benzo (a) anthracene,
Figure G200910013169XD00081
, benzo (b) fluoranthene, benzo (k) fluoranthene
bBenzo (a) pyrene, and dibenzo (a, h) anthracene, benzo (g, h, i) perylene, indeno (1,2,3-cd) pyrene
Relatively can draw by table 2 and table 4; The facilitation that multifactor processing is repaired the Cd-PAHs contaminated soil to black nightshade is better than single factor processing, and handles T9, i.e. low dosage glycine; Glutamic acid and cysteine (Gly+Glu+Cys) mixed liquor is best to the removal effect of above two kinds of polluters; Make black nightshade overground part cadmium content reach 5.65mg/kg, concentration coefficient is compared the cadmium recovery rate and is improved 2.26 times up to 7.9 with contrast; At this moment, the clearance of polycyclic aromatic hydrocarbon also reaches and is up to 34.5% in the soil.Not only satisfied the synthetic required substrate requirement of PCs of plant it is thus clear that the Gly+Glu+Cys of low dosage handles, can also required matrix substrate be provided for the soil microbial degradation polycyclic aromatic hydrocarbon.

Claims (4)

1. one heavy metal species-polycyclic aromatic hydrocarbon combined contamination soil is strengthened renovation agent, and it is characterized in that: its composition is calculated in molar ratio as, glycine: glutamic acid: cysteine=0.1-1.0: 0.1-1.0: 0.1-1.0, and wherein heavy metal is a cadmium;
Said reinforcement renovation agent adds in kind and is implanted with in the heavy metal-polycyclic aromatic hydrocarbon combined contamination soil of super enriching plant and/or enriching plant;
The content 0.3-100mg/kg of heavy metal Cd in the said contaminated soil, the content 0.3-600mg/kg of polycyclic aromatic hydrocarbon PAHs;
Said super enriching plant is a black nightshade.
2. according to the application of the said reinforcement renovation agent of claim 1, it is characterized in that: said reinforcement renovation agent glycine, glutamic acid or the cysteine concentration that adds in contaminated soil is respectively 0.1-1.0mmol/kg soil.
3. according to the application of the said reinforcement renovation agent of claim 1, it is characterized in that: said reinforcement renovation agent glycine, glutamic acid or the cysteine concentration that adds in contaminated soil is respectively 0.2-0.6mmol/kg soil.
4. according to the application of the said reinforcement renovation agent of claim 3, it is characterized in that: said reinforcement renovation agent adds the every kg soil of concentration in contaminated soil, and it is with the soil weight metering of the 0-20 centimetre of dark soil thickness in soil layer surface.
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