CN108841392A - Utilize the conditioner of microorganism remediation organic polluted soil - Google Patents
Utilize the conditioner of microorganism remediation organic polluted soil Download PDFInfo
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- 239000002689 soil Substances 0.000 title claims abstract description 126
- 244000005700 microbiome Species 0.000 title claims abstract description 49
- 238000005067 remediation Methods 0.000 title claims description 25
- 230000000813 microbial effect Effects 0.000 claims abstract description 51
- BFNBIHQBYMNNAN-UHFFFAOYSA-N ammonium sulfate Chemical compound N.N.OS(O)(=O)=O BFNBIHQBYMNNAN-UHFFFAOYSA-N 0.000 claims abstract description 26
- 229910052921 ammonium sulfate Inorganic materials 0.000 claims abstract description 26
- 235000011130 ammonium sulphate Nutrition 0.000 claims abstract description 26
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 claims abstract description 24
- ZPWVASYFFYYZEW-UHFFFAOYSA-L dipotassium hydrogen phosphate Chemical compound [K+].[K+].OP([O-])([O-])=O ZPWVASYFFYYZEW-UHFFFAOYSA-L 0.000 claims abstract description 24
- 229910000402 monopotassium phosphate Inorganic materials 0.000 claims abstract description 23
- 235000019796 monopotassium phosphate Nutrition 0.000 claims abstract description 23
- PJNZPQUBCPKICU-UHFFFAOYSA-N phosphoric acid;potassium Chemical compound [K].OP(O)(O)=O PJNZPQUBCPKICU-UHFFFAOYSA-N 0.000 claims abstract description 23
- 235000019738 Limestone Nutrition 0.000 claims abstract description 22
- 239000006028 limestone Substances 0.000 claims abstract description 22
- 239000001963 growth medium Substances 0.000 claims abstract description 19
- VYPSYNLAJGMNEJ-UHFFFAOYSA-N Silicium dioxide Chemical compound O=[Si]=O VYPSYNLAJGMNEJ-UHFFFAOYSA-N 0.000 claims abstract description 17
- 241000196324 Embryophyta Species 0.000 claims abstract description 13
- OAICVXFJPJFONN-UHFFFAOYSA-N Phosphorus Chemical compound [P] OAICVXFJPJFONN-UHFFFAOYSA-N 0.000 claims abstract description 13
- 229910052698 phosphorus Inorganic materials 0.000 claims abstract description 13
- 239000011574 phosphorus Substances 0.000 claims abstract description 13
- 238000000855 fermentation Methods 0.000 claims abstract description 12
- 230000004151 fermentation Effects 0.000 claims abstract description 12
- 229910052757 nitrogen Inorganic materials 0.000 claims abstract description 12
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 claims abstract description 11
- 229910052799 carbon Inorganic materials 0.000 claims abstract description 11
- 241000193830 Bacillus <bacterium> Species 0.000 claims abstract description 9
- 241000589291 Acinetobacter Species 0.000 claims abstract description 8
- 241000222120 Candida <Saccharomycetales> Species 0.000 claims abstract description 8
- 241000192041 Micrococcus Species 0.000 claims abstract description 8
- 241000609240 Ambelania acida Species 0.000 claims abstract description 7
- 239000010905 bagasse Substances 0.000 claims abstract description 7
- 241000228212 Aspergillus Species 0.000 claims abstract description 6
- 241000223259 Trichoderma Species 0.000 claims abstract description 6
- 239000007788 liquid Substances 0.000 claims abstract 4
- 241000589516 Pseudomonas Species 0.000 claims description 11
- 241000233866 Fungi Species 0.000 claims description 9
- 241000186063 Arthrobacter Species 0.000 claims description 7
- 241000191940 Staphylococcus Species 0.000 claims description 7
- -1 stalk Substances 0.000 claims description 7
- 241000194032 Enterococcus faecalis Species 0.000 claims description 6
- 239000003795 chemical substances by application Substances 0.000 claims description 6
- 229940032049 enterococcus faecalis Drugs 0.000 claims description 6
- 241000590020 Achromobacter Species 0.000 claims description 5
- 241000589565 Flavobacterium Species 0.000 claims description 5
- 241000894006 Bacteria Species 0.000 claims description 4
- 241000187654 Nocardia Species 0.000 claims description 4
- 235000010627 Phaseolus vulgaris Nutrition 0.000 claims 4
- 244000046052 Phaseolus vulgaris Species 0.000 claims 4
- 241000186046 Actinomyces Species 0.000 claims 2
- KDXKERNSBIXSRK-UHFFFAOYSA-N Lysine Natural products NCCCCC(N)C(O)=O KDXKERNSBIXSRK-UHFFFAOYSA-N 0.000 claims 2
- 239000004472 Lysine Substances 0.000 claims 2
- 101100412856 Mus musculus Rhod gene Proteins 0.000 claims 2
- 101100242191 Tetraodon nigroviridis rho gene Proteins 0.000 claims 2
- 241000223230 Trichosporon Species 0.000 claims 2
- 239000003610 charcoal Substances 0.000 claims 2
- 241000186216 Corynebacterium Species 0.000 claims 1
- 241000726221 Gemma Species 0.000 claims 1
- ZLMJMSJWJFRBEC-UHFFFAOYSA-N Potassium Chemical compound [K] ZLMJMSJWJFRBEC-UHFFFAOYSA-N 0.000 claims 1
- 239000002253 acid Substances 0.000 claims 1
- 230000002906 microbiologic effect Effects 0.000 claims 1
- 239000011591 potassium Substances 0.000 claims 1
- 229910052700 potassium Inorganic materials 0.000 claims 1
- 235000019764 Soybean Meal Nutrition 0.000 abstract description 18
- 239000004455 soybean meal Substances 0.000 abstract description 18
- 239000005909 Kieselgur Substances 0.000 abstract description 14
- 239000003864 humus Substances 0.000 abstract description 13
- 239000010902 straw Substances 0.000 abstract description 13
- 239000002957 persistent organic pollutant Substances 0.000 abstract description 8
- 238000005056 compaction Methods 0.000 abstract description 6
- 230000000593 degrading effect Effects 0.000 abstract description 5
- 239000000203 mixture Substances 0.000 abstract description 5
- 235000015097 nutrients Nutrition 0.000 abstract description 5
- 230000008439 repair process Effects 0.000 abstract description 5
- 230000003247 decreasing effect Effects 0.000 abstract description 4
- 238000009423 ventilation Methods 0.000 abstract description 4
- 239000002283 diesel fuel Substances 0.000 description 17
- 239000002609 medium Substances 0.000 description 15
- 239000003607 modifier Substances 0.000 description 12
- 230000000694 effects Effects 0.000 description 10
- 239000002956 ash Substances 0.000 description 8
- 241000316848 Rhodococcus <scale insect> Species 0.000 description 7
- 238000000034 method Methods 0.000 description 7
- 241000282414 Homo sapiens Species 0.000 description 5
- 230000003750 conditioning effect Effects 0.000 description 5
- 238000002360 preparation method Methods 0.000 description 5
- 239000000126 substance Substances 0.000 description 5
- 241000186361 Actinobacteria <class> Species 0.000 description 4
- 241000193386 Lysinibacillus sphaericus Species 0.000 description 4
- 230000008859 change Effects 0.000 description 4
- 241000894007 species Species 0.000 description 4
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- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 4
- 241001465754 Metazoa Species 0.000 description 3
- 230000004060 metabolic process Effects 0.000 description 3
- LWIHDJKSTIGBAC-UHFFFAOYSA-K potassium phosphate Substances [K+].[K+].[K+].[O-]P([O-])([O-])=O LWIHDJKSTIGBAC-UHFFFAOYSA-K 0.000 description 3
- CURLTUGMZLYLDI-UHFFFAOYSA-N Carbon dioxide Chemical compound O=C=O CURLTUGMZLYLDI-UHFFFAOYSA-N 0.000 description 2
- 239000003876 biosurfactant Substances 0.000 description 2
- 230000015556 catabolic process Effects 0.000 description 2
- 230000007812 deficiency Effects 0.000 description 2
- 238000006731 degradation reaction Methods 0.000 description 2
- 229910000396 dipotassium phosphate Inorganic materials 0.000 description 2
- 235000019797 dipotassium phosphate Nutrition 0.000 description 2
- 229910052739 hydrogen Inorganic materials 0.000 description 2
- 239000001257 hydrogen Substances 0.000 description 2
- 238000005259 measurement Methods 0.000 description 2
- 239000003208 petroleum Substances 0.000 description 2
- 241000544230 Dioscorea communis Species 0.000 description 1
- 235000002673 Dioscorea communis Nutrition 0.000 description 1
- 241000282412 Homo Species 0.000 description 1
- UFHFLCQGNIYNRP-UHFFFAOYSA-N Hydrogen Chemical compound [H][H] UFHFLCQGNIYNRP-UHFFFAOYSA-N 0.000 description 1
- 238000013494 PH determination Methods 0.000 description 1
- 230000002378 acidificating effect Effects 0.000 description 1
- 238000005273 aeration Methods 0.000 description 1
- 230000003042 antagnostic effect Effects 0.000 description 1
- 230000008485 antagonism Effects 0.000 description 1
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 1
- 239000001569 carbon dioxide Substances 0.000 description 1
- 229910002092 carbon dioxide Inorganic materials 0.000 description 1
- 150000001875 compounds Chemical class 0.000 description 1
- 238000007796 conventional method Methods 0.000 description 1
- 238000012272 crop production Methods 0.000 description 1
- 238000010586 diagram Methods 0.000 description 1
- 235000014113 dietary fatty acids Nutrition 0.000 description 1
- 238000004945 emulsification Methods 0.000 description 1
- 239000003344 environmental pollutant Substances 0.000 description 1
- 238000011066 ex-situ storage Methods 0.000 description 1
- 238000009313 farming Methods 0.000 description 1
- 239000000194 fatty acid Substances 0.000 description 1
- 229930195729 fatty acid Natural products 0.000 description 1
- 150000004665 fatty acids Chemical class 0.000 description 1
- 239000008187 granular material Substances 0.000 description 1
- 238000011065 in-situ storage Methods 0.000 description 1
- VUZPPFZMUPKLLV-UHFFFAOYSA-N methane;hydrate Chemical compound C.O VUZPPFZMUPKLLV-UHFFFAOYSA-N 0.000 description 1
- 230000007935 neutral effect Effects 0.000 description 1
- 231100000252 nontoxic Toxicity 0.000 description 1
- 230000003000 nontoxic effect Effects 0.000 description 1
- 229910052760 oxygen Inorganic materials 0.000 description 1
- 239000001301 oxygen Substances 0.000 description 1
- 231100000719 pollutant Toxicity 0.000 description 1
- GNSKLFRGEWLPPA-UHFFFAOYSA-M potassium dihydrogen phosphate Chemical compound [K+].OP(O)([O-])=O GNSKLFRGEWLPPA-UHFFFAOYSA-M 0.000 description 1
- 239000000843 powder Substances 0.000 description 1
- 238000002203 pretreatment Methods 0.000 description 1
- 230000008569 process Effects 0.000 description 1
- 230000001105 regulatory effect Effects 0.000 description 1
- 238000005070 sampling Methods 0.000 description 1
- 239000003516 soil conditioner Substances 0.000 description 1
- 238000005728 strengthening Methods 0.000 description 1
- 235000013619 trace mineral Nutrition 0.000 description 1
- 239000011573 trace mineral Substances 0.000 description 1
- 238000011282 treatment Methods 0.000 description 1
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- C—CHEMISTRY; METALLURGY
- C09—DYES; PAINTS; POLISHES; NATURAL RESINS; ADHESIVES; COMPOSITIONS NOT OTHERWISE PROVIDED FOR; APPLICATIONS OF MATERIALS NOT OTHERWISE PROVIDED FOR
- C09K—MATERIALS FOR MISCELLANEOUS APPLICATIONS, NOT PROVIDED FOR ELSEWHERE
- C09K17/00—Soil-conditioning materials or soil-stabilising materials
- C09K17/40—Soil-conditioning materials or soil-stabilising materials containing mixtures of inorganic and organic compounds
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- C—CHEMISTRY; METALLURGY
- C09—DYES; PAINTS; POLISHES; NATURAL RESINS; ADHESIVES; COMPOSITIONS NOT OTHERWISE PROVIDED FOR; APPLICATIONS OF MATERIALS NOT OTHERWISE PROVIDED FOR
- C09K—MATERIALS FOR MISCELLANEOUS APPLICATIONS, NOT PROVIDED FOR ELSEWHERE
- C09K2109/00—MATERIALS FOR MISCELLANEOUS APPLICATIONS, NOT PROVIDED FOR ELSEWHERE pH regulation
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- Chemical & Material Sciences (AREA)
- Inorganic Chemistry (AREA)
- Life Sciences & Earth Sciences (AREA)
- General Life Sciences & Earth Sciences (AREA)
- Soil Sciences (AREA)
- Engineering & Computer Science (AREA)
- Materials Engineering (AREA)
- Organic Chemistry (AREA)
- Soil Conditioners And Soil-Stabilizing Materials (AREA)
- Processing Of Solid Wastes (AREA)
Abstract
本发明利用微生物修复有机污染土壤的调理剂,其组分的质量百分比为:微生物菌群发酵液5~20%;有机改良剂20~50%;培养基30~75%;所述微生物菌群涉及包括不动杆菌属、微球菌属、芽孢杆菌属、假丝酵母属、木霉属、曲霉属在内的19个菌属;所述有机改良剂为硅藻土、腐殖土、秸秆、生物炭、锯末、甘蔗渣、草木灰的一种或几种;所述培养基含有磷酸二氢钾、磷酸氢二钾、硫酸铵、石灰石和豆粕,本发明的调理剂有利于能降解有机污染物的微生物菌群的生长和繁殖,能调节土壤的酸碱度以及碳氮磷的营养配比,有效改善被有机污染土壤的组成和结构,改善土壤因板结而造成通气量下降的状况,从而有效修复被有机污染的土壤。
The present invention utilizes microorganisms to repair the conditioner of organic polluted soil, and the mass percentage of its components is: 5-20% of microbial flora fermentation liquid; 20-50% of organic improver; 30-75% of culture medium; said microbial flora It involves 19 genera including Acinetobacter, Micrococcus, Bacillus, Candida, Trichoderma, and Aspergillus; the organic amendments are diatomaceous earth, humus, straw, One or more of biochar, sawdust, bagasse, and plant ash; the culture medium contains potassium dihydrogen phosphate, dipotassium hydrogen phosphate, ammonium sulfate, limestone and soybean meal, and the conditioner of the present invention is conducive to degrading organic pollutants The growth and reproduction of the microbial flora can adjust the pH of the soil and the nutrient ratio of carbon, nitrogen and phosphorus, effectively improve the composition and structure of the organically polluted soil, and improve the condition of decreased ventilation caused by soil compaction, thereby effectively repairing the contaminated soil. organically polluted soil.
Description
技术领域technical field
本发明属于利用微生物修复被污染土壤的技术领域,具体涉及一种利用微生物修复有机污染、尤其是柴油污染土壤的调理剂。The invention belongs to the technical field of using microorganisms to repair polluted soil, in particular to a conditioner for using microorganisms to restore organic pollution, especially diesel-polluted soil.
背景技术Background technique
土壤是人类、动植物以及微生物赖以生存的必需的自然资源之一。有陆地不一定有土壤,而土壤与人类的生存(农耕和畜牧)密切相关。土壤与环境之间原本存在着一种物质与能量的动态平衡,但随着人类活动的加强和影响,土壤与环境之间的动态平衡逐渐发生了变化:土壤在逐步被污染,其中,有机污染(石油及其产品)对土壤及环境的影响和危害日益严重,被污染的土壤已制约和严重影响到人类、动植物以及微生物的生存。目前,柴油在运输和使用过程中的泄露对土壤构成主要污染。柴油因密度小、粘着力强、乳化能力低的特殊物理化学性质,其进入土壤后很难去除,且残留在土壤中的时间长,使土壤中的碳源大量增加,从而会破坏土壤中原有碳、氮、磷的比值,容易使土壤板结,酸碱度改变,使土壤的结构和组成遭到破坏,从而给污染地区的生态环境、农作物生产和人类的生存带来极大的负面影响。因此,修复被柴油污染的土壤是一项涉及人类生存的重要的工作。目前,修复被有机污染土壤的方法主要有物理化学修复法和生物修复法。而生物修复法又含有微生物修复法及植物修复法,其中,微生物修复法因具有成本低、高效且无二次污染的优势而被广泛采用。Soil is one of the necessary natural resources for human beings, animals, plants and microorganisms to survive. Land does not necessarily have soil, and soil is closely related to human survival (farming and animal husbandry). Originally there was a dynamic balance of matter and energy between the soil and the environment, but with the strengthening and impact of human activities, the dynamic balance between the soil and the environment has gradually changed: the soil is gradually being polluted, among which organic pollution (Petroleum and its products) have increasingly serious impacts and harms on soil and the environment, and polluted soil has restricted and seriously affected the survival of humans, animals, plants, and microorganisms. At present, the leakage of diesel oil during transportation and use constitutes a major pollution to the soil. Due to the special physical and chemical properties of diesel oil with low density, strong adhesion and low emulsification ability, it is difficult to remove after entering the soil, and it remains in the soil for a long time, which greatly increases the carbon source in the soil, thus destroying the original The ratio of carbon, nitrogen, and phosphorus can easily compact the soil, change the pH, and destroy the structure and composition of the soil, which will have a great negative impact on the ecological environment, crop production, and human survival in polluted areas. Therefore, remediation of diesel-contaminated soil is an important work involving human survival. At present, the methods for remediating organically polluted soil mainly include physical chemical remediation and biological remediation. The bioremediation method also includes microbial remediation and phytoremediation. Among them, microbial remediation is widely used because of its advantages of low cost, high efficiency and no secondary pollution.
在微生物修复法中,一般会采用外加调理剂(高效降解菌)、添加适量秸秆、深耕(翻)土壤等措施。从现在的实际效果看,现有微生物修复法还存在一些不足,其主要有:⑴现有的调理剂会对土著菌群产生影响,形成拮抗作用,不利于污染土壤的修复。⑵添加适量秸秆在一定程度上是缓解了土壤的板结、增强了通气量,但是它对被柴油污染的土壤收效甚微。⑶深耕(翻)土壤不仅过程复杂,而且耗时耗力,操作难度大。这些不利因素的出现限制了微生物修复法在被柴油污染土壤修复中的应用,或者说,影响到被柴油污染土壤修复的成效。因此,改进现有的微生物修复法非常有必要。In the microbial remediation method, measures such as adding an external conditioner (high-efficiency degrading bacteria), adding an appropriate amount of straw, and deep plowing (turning) the soil are generally adopted. Judging from the current actual effect, there are still some deficiencies in the existing microbial remediation methods, which mainly include: (1) The existing conditioners will affect the indigenous flora and form an antagonistic effect, which is not conducive to the remediation of contaminated soil. (2) Adding an appropriate amount of straw can relieve soil compaction and enhance ventilation to a certain extent, but it has little effect on soil polluted by diesel oil. (3) Deep plowing (turning) the soil is not only a complicated process, but also time-consuming and labor-intensive, making the operation difficult. The emergence of these unfavorable factors limits the application of microbial remediation in the remediation of diesel-contaminated soil, or in other words, affects the effectiveness of remediation of diesel-contaminated soil. Therefore, it is very necessary to improve the existing microbial remediation method.
发明内容Contents of the invention
本发明的目的在于克服现有技术的不足,提供一种利用微生物修复有机污染土壤的调理剂,它能够有效改善被有机(石油及其产品)污染土壤的组成和结构,调节土壤的酸碱度以及碳、氮、磷的营养配比,改善土壤因板结而造成通气量下降的状况,同时,能添加土著微生物菌群,提高微生物的活性,从而提高利用微生物修复被有机污染土壤的效率。The purpose of the present invention is to overcome the deficiencies in the prior art, to provide a conditioner that utilizes microorganisms to remediate organically polluted soil, which can effectively improve the composition and structure of organic (petroleum and its products) polluted soil, and adjust the pH and carbon content of the soil. The nutrient ratio of nitrogen and phosphorus can improve the situation of decreased ventilation caused by soil compaction. At the same time, it can add indigenous microbial flora to improve the activity of microorganisms, thereby improving the efficiency of using microorganisms to repair organically polluted soil.
本发明的着重点在于构建一个高效的降解菌群。目前污染土壤修复的关键之一是寻找到能够相互协同作用的高效降解菌群,使其能够在复杂的、被有机污染的土壤中发挥作用,通过微生物的代谢过程将土壤中的有机污染物转化成无毒的脂肪酸、二氧化碳和水。The focus of the present invention is to construct an efficient degrading bacteria group. At present, one of the keys to remediation of contaminated soil is to find efficient degrading bacteria groups that can interact with each other, so that they can play a role in complex and organically polluted soils, and transform organic pollutants in soil through microbial metabolic processes. into non-toxic fatty acids, carbon dioxide and water.
为实现上述目的,本发明采取了以下技术方案。In order to achieve the above object, the present invention adopts the following technical solutions.
一种利用微生物修复有机污染土壤的调理剂,其特征在于,含有微生物菌群、有机改良剂和培养基,所述调理剂组分的质量百分比为:A conditioner utilizing microorganisms to remediate organically polluted soil is characterized in that it contains microbial flora, an organic amendment and a culture medium, and the mass percentage of the conditioner component is:
微生物菌群发酵液(OD=1.5~3) 5~20%;Microbial flora fermentation broth (OD=1.5~3) 5~20%;
有机改良剂 20~50%;Organic modifier 20-50%;
培养基 30~75%。Medium 30-75%.
进一步,所述微生物菌群为不动杆菌属(Acinetobacter)、微球菌属(Micrococcus)、芽孢杆菌属(Bacillus)、放线菌属(Actinomycetes)、假单胞菌属(pseudomonas)、红球菌属(Rhodococcus)、棒杆菌属(Coryneforms)、粪肠球菌属(Enterococcus faecalis)、葡萄球菌属(Staphylococcus)、黄杆菌属(Flavobacterium)、无色杆菌属(Achromobacter)、赖氨酸芽孢杆菌属(Lysinibacillus sphaericus)、节细菌属(Arthrobacter)、诺卡氏菌属(Nocardia)、假丝酵母属(Candida)、丝孢酵母属(Trichos)、木霉属(Trichoderma)、曲霉属(Aspergillus)、白腐真菌属(write-rotfungi)。Further, the microbial flora is Acinetobacter, Micrococcus, Bacillus, Actinomycetes, Pseudomonas, Rhodococcus (Rhodococcus), Coryneforms, Enterococcus faecalis, Staphylococcus, Flavobacterium, Achromobacter, Lysinibacillus sphaericus), Arthrobacter, Nocardia, Candida, Trichos, Trichoderma, Aspergillus, white rot Fungi (write-rot fungi).
进一步,所述有机改良剂为硅藻土、腐殖土、秸秆、生物炭、锯末、甘蔗渣、草木灰的一种或几种。Furthermore, the organic modifier is one or more of diatomaceous earth, humus, straw, biochar, sawdust, bagasse, and plant ash.
进一步,所述培养基为磷酸二氢钾、磷酸氢二钾、硫酸铵、石灰石和豆粕,它们占所述组分的质量百分比为:Further, the medium is potassium dihydrogen phosphate, dipotassium hydrogen phosphate, ammonium sulfate, limestone and soybean meal, and their mass percentages in the components are:
进一步,将所述磷酸二氢钾和所述磷酸氢二钾作为磷源,将所述硫酸铵作为氮源,将土壤中碳:氮:磷(C:N:P)的比例调节为100~120:10~12:1。Further, the potassium dihydrogen phosphate and the dipotassium hydrogen phosphate are used as a phosphorus source, and the ammonium sulfate is used as a nitrogen source, and the ratio of carbon in the soil: nitrogen: phosphorus (C:N:P) is adjusted to 100~ 120:10~12:1.
一种利用微生物修复有机污染土壤的调理剂,其特征在于,含有微生物菌群、有机改良剂和培养基,所述微生物菌群包括不动杆菌属(Acinetobacter)、微球菌属(Micrococcus)、芽孢杆菌属(Bacillus)、放线菌属(Actinomycetes)、假单胞菌属(pseudomonas)、红球菌属(Rhodococcus)、棒杆菌属(Coryneforms)、粪肠球菌属(Enterococcus faecalis)、葡萄球菌属(Staphylococcus)、黄杆菌属(Flavobacterium)、无色杆菌属(Achromobacter)、赖氨酸芽孢杆菌属(Lysinibacillus sphaericus)、节细菌属(Arthrobacter)、诺卡氏菌属(Nocardia)、假丝酵母属(Candida)、丝孢酵母属(Trichos)、木霉属(Trichoderma)、曲霉属(Aspergillus)、白腐真菌属(write-rot fungi)多属的组合;所述培养基含有磷酸二氢钾、磷酸氢二钾、硫酸铵、石灰石和豆粕;所述调理剂组分的质量百分比为:A conditioner utilizing microorganisms to remediate organic polluted soil is characterized in that it contains microbial flora, an organic amendment and a culture medium, and said microbial flora includes Acinetobacter (Acinetobacter), Micrococcus (Micrococcus), spore Bacillus, Actinomycetes, Pseudomonas, Rhodococcus, Coryneforms, Enterococcus faecalis, Staphylococcus ( Staphylococcus), Flavobacterium, Achromobacter, Lysinibacillus sphaericus, Arthrobacter, Nocardia, Candida ( Candida), Trichos, Trichoderma, Aspergillus, and write-rot fungi; Dipotassium hydrogen, ammonium sulfate, limestone and soybean meal; the mass percentage of described conditioning agent component is:
微生物菌群发酵液 5~20%;Microbial flora fermentation broth 5-20%;
有机改良剂 20~50%;Organic modifier 20-50%;
培养基 30~75%。Medium 30-75%.
进一步,所述磷酸二氢钾、磷酸氢二钾、硫酸铵、石灰石和豆粕占所述组分的质量百分比分别为:Further, the mass percentages of potassium dihydrogen phosphate, dipotassium hydrogen phosphate, ammonium sulfate, limestone and soybean meal accounting for the components are respectively:
本发明利用微生物修复有机污染土壤的调理剂的积极效果是:The present invention utilizes the active effect of the conditioner of microorganism repairing organic polluted soil to be:
(1)本发明采用的微生物菌群,是将不同属的微生物组合在一起并进行了优化,所述不同属的微生物属于土壤中常见的微生物,因此,不存在与土著微生物产生拮抗作用的问题;通过不同属微生物之间良好的协同作用能有效地降解有机污染物,它不仅适用于低浓度有机污染物的土壤,而且对于高浓度以及复合型浓度的有机污染物土壤也能有一定的修复作用。(1) The microbial flora used in the present invention is to combine and optimize the microorganisms of different genera. The microorganisms of different genera belong to the common microorganisms in the soil, so there is no problem of antagonism with the indigenous microorganisms It can effectively degrade organic pollutants through the good synergy between different genera of microorganisms. It is not only suitable for soils with low concentrations of organic pollutants, but also can repair soils with high concentrations and compound concentrations of organic pollutants. effect.
(2)采用的有机改良剂为硅藻土、腐殖土、秸秆、生物炭、锯末、甘蔗渣、草木灰的一种或几种,它们既有土壤微生物生长的微量元素以及少量的能源,同时还能够疏松土壤,缓解土壤的板结现象。(2) The organic amendments used are one or more of diatomite, humus, straw, biochar, sawdust, bagasse, and plant ash. They have both trace elements and a small amount of energy for soil microbial growth, and at the same time It can also loosen the soil and relieve the compaction of the soil.
(3)采用含有磷酸二氢钾、磷酸氢二钾、硫酸铵的培养基;由于被有机污的土壤中积累了大量的碳源,因此,本发明的调理剂将磷酸二氢钾和磷酸氢二钾作为磷源,将硫酸铵作为氮源,能通过添加适当的磷酸二氢钾、磷酸氢二钾和硫酸铵将土壤中碳:氮:磷的比例调节为100~120:10~12:1,这个比例有利于所述微生物菌群的生长和繁殖。(3) adopt the culture medium that contains potassium dihydrogen phosphate, dipotassium hydrogen phosphate, ammonium sulfate; Because a large amount of carbon sources have been accumulated in the soil of organic pollution, therefore, conditioner of the present invention combines potassium dihydrogen phosphate and hydrogen phosphate Dipotassium is used as a phosphorus source, and ammonium sulfate is used as a nitrogen source. By adding appropriate potassium dihydrogen phosphate, dipotassium hydrogen phosphate and ammonium sulfate, the ratio of carbon: nitrogen: phosphorus in the soil can be adjusted to 100-120:10-12: 1. This ratio is conducive to the growth and reproduction of the microbial flora.
(4)本发明的培养基中含有石灰石,它是作为土壤酸碱度的调节剂使用的,能保持土壤呈现中性或者偏碱性,从而有利于所述微生物菌群的生长和繁殖,同时还能够改善土壤的板结现象,有利于土壤通气,提供足够的氧气量。(4) The culture medium of the present invention contains limestone, which is used as a regulator of soil pH and can keep the soil neutral or slightly alkaline, thereby facilitating the growth and reproduction of the microbial flora, while also being able to Improve soil compaction, facilitate soil aeration and provide sufficient oxygen.
(5)本发明的培养基中含有豆粕,它能提供生物表面活性剂中的一种或多种,能将土壤中的难以溶解于水中的有机污染物乳化,降低其表面张力,增加微生物菌群与有机污染物的界面张力。由豆粕提供的生物表面活性剂对环境友好,不会造成二次污染。(5) The culture medium of the present invention contains soybean meal, which can provide one or more biosurfactants, which can emulsify organic pollutants in the soil that are difficult to dissolve in water, reduce its surface tension, and increase microbial growth. Interfacial tension between groups and organic pollutants. The biosurfactant provided by soybean meal is friendly to the environment and will not cause secondary pollution.
(6)本发明的调理剂,有利于能降解有机污染物的微生物菌群的生长和繁殖,能调节土壤的酸碱度以及碳氮磷的营养配比,有效改善被有机污染土壤的组成和结构,改善土壤因板结而造成通气量下降的状况,从而有效修复被有机污染的土壤。(6) Conditioning agent of the present invention is conducive to the growth and reproduction of microbial flora capable of degrading organic pollutants, can regulate the pH of soil and the nutrient ratio of carbon, nitrogen and phosphorus, and effectively improve the composition and structure of organically polluted soil, Improve the condition of decreased ventilation caused by soil compaction, so as to effectively restore organically polluted soil.
附图说明Description of drawings
图1为本发明应用实施例1被柴油污染土壤添加本发明的调理剂后pH的变化。Fig. 1 is the change of pH after the conditioner of the present invention is added to soil polluted by diesel oil in application example 1 of the present invention.
图2为本发明应用实施例1被有机污染土壤修复的效果示意图。Fig. 2 is a schematic diagram of the effect of remediation of organically polluted soil in Application Example 1 of the present invention.
具体实施方式Detailed ways
以下给出本发明利用微生物修复有机污染土壤的调理剂的具体实施方式,提供6个实施例和1个应用实施例。但是应当指出,本发明的实施不限于以下的实施方式。本发明的调理剂在实际应用时,应该根据土壤的污染程度、土壤的酸碱度、土壤中营养成分的差异进行适当调整。The specific implementation of the conditioner for remediating organic polluted soil by using microorganisms of the present invention is given below, providing 6 examples and 1 application example. However, it should be noted that implementation of the present invention is not limited to the following embodiments. When the conditioning agent of the present invention is used in practice, it should be properly adjusted according to the degree of pollution of the soil, the pH of the soil, and the difference in nutrients in the soil.
实施例1Example 1
(一)一种利用微生物修复有机污染土壤的调理剂,含有微生物菌群、有机改良剂和培养基,所述微生物菌群为不动杆菌属(Acinetobacter)、微球菌属(Micrococcus)、芽孢杆菌属(Bacillus)、假单胞菌属(pseudomonas)和无色杆菌属(Achromobacter)五种的组合;所述有机改良剂为硅藻土、草木灰、腐殖土、秸秆、锯末的组合;所述培养基为磷酸二氢钾、磷酸氢二钾、硫酸铵、石灰石和豆粕的组合。(1) A conditioner utilizing microorganisms to remediate organically polluted soil, containing microbial flora, organic amendments and culture medium, said microbial flora being Acinetobacter (Acinetobacter), Micrococcus (Micrococcus), Bacillus A combination of five species of genus Bacillus, pseudomonas and Achromobacter; the organic modifier is a combination of diatomaceous earth, plant ash, humus, straw, and sawdust; the The medium is a combination of potassium dihydrogen phosphate, dipotassium hydrogen phosphate, ammonium sulfate, limestone and soybean meal.
所述调理剂组分的质量百分比为:The mass percentage of described conditioner component is:
微生物菌群发酵液(OD=1.5) 5%;Microbial flora fermentation broth (OD=1.5) 5%;
有机改良剂50%,其中:硅藻土20%、草木灰10%、腐殖土10%、秸秆5%、锯末5%;50% organic modifier, including: 20% diatomaceous earth, 10% plant ash, 10% humus, 5% straw, and 5% sawdust;
培养基45%,其中:磷酸二氢钾12%、磷酸氢二钾8%、硫酸铵19%、石灰石5%、豆粕1%。Medium 45%, including: potassium dihydrogen phosphate 12%, dipotassium hydrogen phosphate 8%, ammonium sulfate 19%, limestone 5%, soybean meal 1%.
(二)将所述微生物菌群、有机改良剂和培养基质量百分比的组分用常规方法进行制备,获得本发明的利用微生物修复有机污染土壤的调理剂,所述调理剂应该是颗粒或粉末状态的。(2) The components of the microbial flora, the organic amendment and the mass percentage of the medium are prepared by a conventional method to obtain the conditioner of the present invention utilizing microorganisms to remediate organically polluted soil, and the conditioner should be granules or powders status.
(三)本发明利用微生物修复有机污染土壤的调理剂的使用(3) The present invention utilizes the use of the conditioner of microorganism repairing organic polluted soil
本发明的调理剂既可用于原位处理,也可用于异位处理。The conditioners of the present invention can be used in both in situ and ex situ treatments.
使用前应先清除阻碍土壤翻耕的较大的物体,并要有足够的水源。Larger objects that hinder soil plowing should be removed before use, and sufficient water should be provided.
将本发明的调理剂抛洒到有机污染的土壤中,土壤的含水率以20-50%为最佳。Sprinkle the conditioning agent of the present invention into organically polluted soil, and the moisture content of the soil is optimal at 20-50%.
实施例2Example 2
(一)一种利用微生物修复有机污染土壤的调理剂,含有微生物菌群、有机改良剂和培养基,所述微生物菌群为放线菌属(Actinomycetes)、假单胞菌属(pseudomonas)、红球菌属(Rhodococcus)、棒杆菌属(Coryneforms)、假丝酵母属(Candida)五种的组合;所述有机改良剂为硅藻土、草木灰、腐殖土、甘蔗渣和锯末的组合;所述培养基含有磷酸二氢钾、磷酸氢二钾、硫酸铵、石灰石和豆粕。(1) A conditioner utilizing microorganisms to remediate organically polluted soil, containing microbial flora, organic amendments and culture medium, said microbial flora being Actinomycetes (Actinomycetes), Pseudomonas (pseudomonas), The combination of Rhodococcus (Rhodococcus), Coryneforms (Coryneforms), and Candida (Candida); the organic amendment is a combination of diatomaceous earth, plant ash, humus, bagasse and sawdust; The medium contained monopotassium phosphate, dipotassium phosphate, ammonium sulfate, limestone and soybean meal.
所述调理剂组分的质量百分比为:The mass percentage of described conditioner component is:
微生物菌群发酵液(OD=2.0) 10%;Microbial flora fermentation broth (OD=2.0) 10%;
有机改良剂45%,其中,硅藻土15%、草木灰15%,腐殖土7%,甘蔗渣5%,锯末3%;45% organic modifier, including 15% diatomaceous earth, 15% plant ash, 7% humus, 5% bagasse, and 3% sawdust;
培养基45%,其中,磷酸二氢钾10%、磷酸氢二钾5%、硫酸铵13%、石灰石15%、豆粕2%。45% medium, including 10% potassium dihydrogen phosphate, 5% dipotassium hydrogen phosphate, 13% ammonium sulfate, 15% limestone, and 2% soybean meal.
(二)本发明利用微生物修复有机污染土壤的调理剂的制备(同实施例1)。(2) The present invention utilizes the preparation of the conditioner of microorganism repairing organic polluted soil (same as embodiment 1).
(三)本发明利用微生物修复有机污染土壤的调理剂的使用(同实施例1)。(3) The present invention utilizes the use of the conditioner of microorganism repairing organic polluted soil (same as embodiment 1).
实施例3Example 3
(一)一种利用微生物修复有机污染土壤的调理剂,含有微生物菌群、有机改良剂和培养基,所述微生物菌群为粪肠球菌属(Enterococcus faecalis)、葡萄球菌属(Staphylococcus)、黄杆菌属(Flavobacterium)、白腐真菌(write-rot fungi)四种的组合;所述有机改良剂为硅藻土、草木灰、生物炭和锯末的组合;所述培养基含有磷酸二氢钾、磷酸氢二钾、硫酸铵、石灰石和豆粕。(1) A conditioner that utilizes microorganisms to remediate organically polluted soil contains microbial flora, an organic amendment and a culture medium, and the microbial flora is Enterococcus faecalis (Enterococcus faecalis), Staphylococcus (Staphylococcus), yellow Bacillus (Flavobacterium), white rot fungi (write-rot fungi) four kinds of combinations; the organic amendment is a combination of diatomaceous earth, plant ash, biochar and sawdust; the medium contains potassium dihydrogen phosphate, phosphoric acid Dipotassium hydrogen, ammonium sulfate, limestone and soybean meal.
所述调理剂组分的质量百分比为:The mass percentage of described conditioner component is:
微生物菌群发酵液(OD=2.5) 15%;Microbial flora fermentation broth (OD=2.5) 15%;
有机改良剂30%,其中,硅藻土17%、草木灰2%、生物炭10%、锯末1%;30% organic modifier, including 17% diatomaceous earth, 2% plant ash, 10% biochar, and 1% sawdust;
培养基55%,其中,磷酸二氢钾8%,磷酸氢二钾2%、硫酸铵1%、石灰石40%、豆粕4%。Medium 55%, including 8% potassium dihydrogen phosphate, 2% dipotassium hydrogen phosphate, 1% ammonium sulfate, 40% limestone, and 4% soybean meal.
(二)本发明利用微生物修复有机污染土壤的调理剂的制备(同实施例1)。(2) The present invention utilizes the preparation of the conditioner of microorganism repairing organic polluted soil (same as embodiment 1).
(三)本发明利用微生物修复有机污染土壤的调理剂的使用(同实施例1)。(3) The present invention utilizes the use of the conditioner of microorganism repairing organic polluted soil (same as embodiment 1).
实施例4Example 4
一种利用微生物修复有机污染土壤的调理剂,含有微生物菌群、有机改良剂和培养基,所述微生物菌群为赖氨酸芽孢杆菌属(Lysinibacillus sphaericus)、节细菌属(Arthrobacter)、诺卡氏菌属(Nocardia)、木霉属(Trichoderma)、曲霉属(Aspergillus)五种的组合;所述有机改良剂为硅藻土、腐殖土、秸秆三种的组合;所述培养基含有磷酸二氢钾、磷酸氢二钾、硫酸铵、石灰石和豆粕。A conditioner for utilizing microorganisms to remediate organically polluted soil, containing microbial flora, an organic amendment and a culture medium, said microbial flora being Lysinibacillus sphaericus, Arthrobacter, Norca A combination of five species of Nocardia, Trichoderma, and Aspergillus; the organic amendment is a combination of diatomaceous earth, humus, and straw; the medium contains phosphoric acid Potassium dihydrogen, dipotassium phosphate, ammonium sulfate, limestone and soybean meal.
所述调理剂组分的质量百分比为:The mass percentage of described conditioner component is:
微生物菌群发酵液(OD=3.0)20%;Microbial flora fermentation broth (OD=3.0) 20%;
有机改良剂20%,其中,硅藻土7%、腐殖土10%、秸秆3%;20% organic modifier, including 7% diatomaceous earth, 10% humus, and 3% straw;
培养基60%,其中,磷酸二氢钾5%,磷酸氢二钾11%、硫酸铵9%、石灰石30%、豆粕5%。Medium 60%, including 5% potassium dihydrogen phosphate, 11% dipotassium hydrogen phosphate, 9% ammonium sulfate, 30% limestone, and 5% soybean meal.
(二)本发明利用微生物修复有机污染土壤的调理剂的制备(同实施例1)。(2) The present invention utilizes the preparation of the conditioner of microorganism repairing organic polluted soil (same as embodiment 1).
(三)本发明利用微生物修复有机污染土壤的调理剂的使用(同实施例1)。(3) The present invention utilizes the use of the conditioner of microorganism repairing organic polluted soil (same as embodiment 1).
实施例5Example 5
一种利用微生物修复有机污染土壤的调理剂,含有微生物菌群、有机改良剂和培养基,所述微生物菌群为赖氨酸芽孢杆菌属(Lysinibacillus sphaericus)、红球菌属(Rhodococcus)、节细菌属(Arthrobacter)三种的组合;所述有机改良剂为硅藻土、腐殖土、秸秆三种的组合;所述培养基含有磷酸二氢钾、磷酸氢二钾、硫酸铵、石灰石和豆粕。A conditioner for utilizing microorganisms to remediate organically polluted soil, containing microbial flora, an organic amendment and a culture medium, said microbial flora being Lysinibacillus sphaericus, Rhodococcus, Arthrobacter A combination of three species of Arthrobacter; the organic modifier is a combination of diatomaceous earth, humus, and straw; the culture medium contains potassium dihydrogen phosphate, dipotassium hydrogen phosphate, ammonium sulfate, limestone and soybean meal .
所述调理剂组分的质量百分比为:The mass percentage of described conditioner component is:
微生物菌群发酵液(OD=1.5) 5%;Microbial flora fermentation broth (OD=1.5) 5%;
有机改良剂20%,其中,硅藻土5%、腐殖土12%、秸秆3%;20% organic modifier, including 5% diatomaceous earth, 12% humus, and 3% straw;
培养基75%,其中,磷酸二氢钾15%,磷酸氢二钾7%、硫酸铵20%、石灰石30%、豆粕3%。Medium 75%, including 15% potassium dihydrogen phosphate, 7% dipotassium hydrogen phosphate, 20% ammonium sulfate, 30% limestone, and 3% soybean meal.
(二)本发明利用微生物修复有机污染土壤的调理剂的制备(同实施例1)。(2) The present invention utilizes the preparation of the conditioner of microorganism repairing organic polluted soil (same as embodiment 1).
(三)本发明利用微生物修复有机污染土壤的调理剂的使用(同实施例1)。(3) The present invention utilizes the use of the conditioner of microorganism repairing organic polluted soil (same as embodiment 1).
实施例6Example 6
一种利用微生物修复有机污染土壤的调理剂,含有微生物菌群、有机改良剂和培养基,所述微生物菌群为白腐真菌(write-rot fungi)、假单胞菌属(pseudomonas)、红球菌属(Rhodococcus)三种的组合;所述有机改良剂为硅藻土、腐殖土、生物炭、秸秆、锯末五种的组合;所述培养基含有磷酸二氢钾、磷酸氢二钾、硫酸铵、石灰石和豆粕。A conditioner for utilizing microorganisms to remediate organically polluted soil, containing microbial flora, organic amendments and culture medium, said microbial flora is white-rot fungi (write-rot fungi), pseudomonas (pseudomonas), red A combination of three species of Rhodococcus; the organic modifier is a combination of diatomaceous earth, humus, biochar, straw, and sawdust; the medium contains potassium dihydrogen phosphate, dipotassium hydrogen phosphate, Ammonium sulfate, limestone and soybean meal.
所述调理剂组分的质量百分比为:The mass percentage of described conditioner component is:
微生物菌群发酵液(OD=2.0) 20%;Microbial flora fermentation broth (OD=2.0) 20%;
有机改良剂50%,其中,硅藻土15%、腐殖土20%、生物炭10%、秸秆3%、锯末2%;50% organic modifier, including 15% diatomaceous earth, 20% humus, 10% biochar, 3% straw, and 2% sawdust;
培养基30%,其中,磷酸二氢钾5%,磷酸氢二钾4%、硫酸铵10%、石灰石10%、豆粕1%。30% medium, including 5% potassium dihydrogen phosphate, 4% dipotassium hydrogen phosphate, 10% ammonium sulfate, 10% limestone, and 1% soybean meal.
(二)本发明利用微生物修复有机污染土壤的调理剂的制备(同实施例1)。(2) The present invention utilizes the preparation of the conditioner of microorganism repairing organic polluted soil (same as embodiment 1).
(三)本发明利用微生物修复有机污染土壤的调理剂的使用(同实施例1)。(3) The present invention utilizes the use of the conditioner of microorganism repairing organic polluted soil (same as embodiment 1).
应用实施例1Application Example 1
应用本发明实施例2提供的利用微生物修复有机污染土壤的调理剂修复被柴油污染的土壤。Apply the conditioner for remediating organic polluted soil with microorganisms provided in Example 2 of the present invention to remediate soil contaminated by diesel oil.
(1)土壤前期处理:清除阻碍土壤翻耕的较大的物体,设置足够的水源。(1) Pre-treatment of soil: remove larger objects that hinder soil plowing, and set up sufficient water sources.
(2)设置应用实施区域和对照区域:为了方便测定的进行,对修复的区域进行划分和明确:设置3个应用实施区域,每个区域为1平方米;3个不应用实施的对照区域,每个区域也为1平方米。(2) Set application implementation area and control area: in order to facilitate the measurement, divide and clarify the repaired area: set 3 application implementation areas, each area is 1 square meter; 3 control areas without application implementation, Each area is also 1 square meter.
(3)取样测定被污染土壤的理化性质及其土壤中柴油的含量。(3) Sampling to determine the physical and chemical properties of the polluted soil and the content of diesel in the soil.
(4)进行翻耕,翻耕深度为30厘米。(4) Carry out plowing, the plowing depth is 30 centimetres.
(5)将本发明的调理剂按照3%的浓度比例抛洒到3个应用实施区域被柴油污染的土壤中,土壤的含水率以20-50%为最佳。(5) Sprinkle the conditioning agent of the present invention into the soil polluted by diesel oil in 3 application implementation areas according to the concentration ratio of 3%, and the moisture content of the soil is optimal at 20-50%.
(6)利用磷酸二氢钾和磷酸氢二钾的磷源,利用硫酸铵的氮源,将土壤中碳∶氮∶磷的比例调节为100~120∶10~12∶1之间,定时测定土壤中pH及残余柴油含量的测定。(6) Utilize the phosphorus source of potassium dihydrogen phosphate and dipotassium hydrogen phosphate, and utilize the nitrogen source of ammonium sulfate to adjust the ratio of carbon: nitrogen: phosphorus in the soil to between 100~120:10~12:1, and measure regularly Determination of pH and residual diesel content in soil.
应用实施例1对被柴油污染土壤的理化性质的测定结构见表1。See Table 1 for the measurement structure of the physical and chemical properties of soil contaminated by diesel oil in Application Example 1.
表1.应用实施例1中被柴油污染土壤的理化性质Table 1. Physicochemical properties of soil polluted by diesel oil in application example 1
从表1中我们可以看出:被柴油污染土壤呈碱性,且土壤中营养含量的比例不协调,因此,被柴油污染的土壤是不适合农作物生长和不利于微生物菌群生长代谢的。From Table 1, we can see that the soil polluted by diesel oil is alkaline, and the proportion of nutrients in the soil is uncoordinated. Therefore, the soil polluted by diesel oil is not suitable for the growth of crops and the growth and metabolism of microbial flora.
应用实施例1中被柴油污染土壤添加本发明的调理剂后pH的变化见图1。See Figure 1 for the change in pH after the conditioner of the present invention is added to the soil polluted by diesel oil in Application Example 1.
从图1中pH的变化我们可以看出:添加土壤调理剂的实验组的pH最终保持在7左右,这是因为添加的调理剂中有石灰石的作用,此外,微生物菌群在利用柴油作为碳源的同时也产生了酸性物质,会使土壤中的pH下降,这是有利于微生物菌群生长的。而在对照组中,土壤的pH几乎没有变化,因此能说明,本发明实施例2提供的利用微生物修复有机污染土壤的调理剂能够起到调节土壤酸碱度的作用。From the change of pH in Figure 1, we can see that the pH of the experimental group added with soil conditioner is finally maintained at about 7, this is because the added conditioner has the effect of limestone, in addition, microbial flora is using diesel oil as carbon At the same time, it also produces acidic substances, which will lower the pH of the soil, which is conducive to the growth of microbial flora. In the control group, the pH of the soil hardly changed, so it can be explained that the conditioner for using microorganisms to remediate organic polluted soil provided by Example 2 of the present invention can play a role in regulating the pH of the soil.
应用实施例1中被柴油污染土壤修复的效果见图2。The effect of remediation of diesel-contaminated soil in Application Example 1 is shown in Figure 2.
从图2可以看出,随着时间的延长,被柴油污染土壤中柴油的含量在下降,柴油的降解率在修复的第38天达到了72%,而对照组虽然也有少部分柴油被降解,但其降解的速度较实验组慢很多,修复的效果非常明显。因此可以证明:添加本发明实施例2提供的利用微生物修复有机污染土壤的调理剂对修复被柴油污染的土壤是非常有效的。It can be seen from Figure 2 that with the extension of time, the content of diesel oil in the soil polluted by diesel oil decreased, and the degradation rate of diesel oil reached 72% on the 38th day of restoration, while a small part of diesel oil was degraded in the control group. However, its degradation rate is much slower than that of the experimental group, and the repair effect is very obvious. Therefore, it can be proved that adding the conditioner for remediating organic polluted soil by using microorganisms provided in Example 2 of the present invention is very effective for remediating soil contaminated by diesel oil.
应用实施例1的结果表明:本发明的利用微生物修复有机污染土壤的调理剂能够为微生物菌群提供良好的生长代谢环境,同时能改善土壤的组成、结构以及土壤的孔隙率,能有效地降解有机(柴油)污染物。The results of Application Example 1 show that the conditioner utilizing microorganisms to remediate organically polluted soil of the present invention can provide a good growth and metabolism environment for microbial flora, and can simultaneously improve the composition, structure and porosity of soil, and can effectively degrade Organic (diesel) pollutants.
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