CN105960446B - Microorganism compositionss - Google Patents

Microorganism compositionss Download PDF

Info

Publication number
CN105960446B
CN105960446B CN201580003186.9A CN201580003186A CN105960446B CN 105960446 B CN105960446 B CN 105960446B CN 201580003186 A CN201580003186 A CN 201580003186A CN 105960446 B CN105960446 B CN 105960446B
Authority
CN
China
Prior art keywords
mass
microorganism
glycerol
compositionss
sorbitol
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.)
Active
Application number
CN201580003186.9A
Other languages
Chinese (zh)
Other versions
CN105960446A (en
Inventor
安藤卓也
清水巧治
当田纪贤
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.)
Panasonic Intellectual Property Management Co Ltd
Original Assignee
Panasonic Intellectual Property Management Co Ltd
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 Panasonic Intellectual Property Management Co Ltd filed Critical Panasonic Intellectual Property Management Co Ltd
Publication of CN105960446A publication Critical patent/CN105960446A/en
Application granted granted Critical
Publication of CN105960446B publication Critical patent/CN105960446B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Classifications

    • BPERFORMING OPERATIONS; TRANSPORTING
    • B09DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
    • B09BDISPOSAL OF SOLID WASTE NOT OTHERWISE PROVIDED FOR
    • B09B3/00Destroying solid waste or transforming solid waste into something useful or harmless
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F3/00Biological treatment of water, waste water, or sewage

Landscapes

  • Life Sciences & Earth Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Chemical & Material Sciences (AREA)
  • Microbiology (AREA)
  • Organic Chemistry (AREA)
  • Water Supply & Treatment (AREA)
  • Hydrology & Water Resources (AREA)
  • Biodiversity & Conservation Biology (AREA)
  • Processing Of Solid Wastes (AREA)
  • Materials Engineering (AREA)
  • Soil Sciences (AREA)
  • General Life Sciences & Earth Sciences (AREA)
  • Treatment Of Biological Wastes In General (AREA)
  • Micro-Organisms Or Cultivation Processes Thereof (AREA)
  • Soil Conditioners And Soil-Stabilizing Materials (AREA)

Abstract

The present invention relates to microorganism compositionss.The presence of microorganism compositionss is placed on the situation of outdoor together with transport container after being transported to soil sanitation scene, the phenomenon of crystallization occurs in transport container when being placed several weeks.A kind of microorganism compositionss it is characterised in that described microorganism can purification soil, the organochlorine compound in subsoil water, described microorganism compositionss are by the sugar alcohol selected from more than a kind in Sorbitol, mannitol, xylitol;Glycerol;Nonionic surfactant;And water is constituted, the containing ratio of aforementioned sugar alcohol is less than 6 times of aforementioned glycerol, even if described microorganism compositionss are placed together with transport container in outdoor, also will not be in container intercrystalline.

Description

Microorganism compositionss
Technical field
The present invention relates in order to using the organochlorine compound in microbial decomposition soil and groundwater come purification soil and Subsoil water and be injected into the microorganism compositionss in soil and groundwater.
Background technology
Because being by the problem of the soil and groundwater of chemical contamination, not only breaking up the mankind, also to destroy biosphere whole The balance of body, from the viewpoint of environmental conservation, needs certain countermeasure.In addition, contaminated soil and subsoil water are put no Reason, is related to that mankind's activity scope is restricted, is also required to countermeasure from economic point of view.
In the past, in order to purify by the soil and groundwater of chemical contamination it is proposed that lime method, Powder by Iron Powder, soil are opened Dig the various methods such as cushion, soil wet soil formula ablution, biological degradation method.The pollution great majority of soil and groundwater are big model Enclose the situation of diffusion, change the scale of method of the earth that bankets itself and expense becomes huge.
Generally acknowledged as do not need large-scale engineering and in original place economically one of method of purification soil and subsoil water Biological degradation method is suitable.It is to make aerobism in soil and groundwater or anaerobic microbial decomposition as pollutant The method of the chemical substance of matter.
For example, the microorganism of fusobacterium in anaerobism atmosphere decomposing organic matter and be decomposed into acetic acid etc..Release in this operation Hydrogen.This hydrogen can replace chloroform, dichloromethane, dichloroethanes, the chlorine of trichloro ethylene such organochlorine based compound, thus only Change these chemical substances.That is, can be to organochlorine based compound using the reduction reaction that the hydrogen producing under anaerobism atmosphere causes Carry out dechlorination to purify chemical substance.
Propose and produced hydrogen as above and provide the material group of hydrogen to be referred to as hydrogen donor, and the same of activation of microorganism will be made The material group (hereinafter referred to as " nutrient source ") of Shi Chengwei hydrogen donor is injected into the method in soil and groundwater.Such nutrient source The worry of the secondary pollution that the part beyond being diffused into impurely when there is excessive injection is led to.Thus, for example patent documentation 1 In disclose make straight chain fatty acid be mixed into make granular straight chain fatty acid, in glycerol so that it is not easy to move from injection place Dynamic compositionss out.
It is well known, however, that microorganism can inactivate it has to by the nutrition after extreme dilution under the nutrient source of high concentration on the contrary Source is sent in soil and groundwater.If in addition, nutrient source is also close to natural materials, small toxicity and without having to worry about secondary dirt Dye.Then it is proposed that viscosity is low, in soil and underground on the contrary compared with not from embedded the solidss being moved, gel The method spreading in water and widely providing nutrient source from 1 well.
Patent Document 2 discloses by the nutrient source based on Sorbitol be diluted to 2000ppm and send into soil and So that the technology of microbial decomposition organochlorine compound in subsoil water.More specifically, by Sorbitol 60%, glycerol 10%, Anion 2%, the nutrient source of water 28% are diluted to 2000ppm and send into and so that it is spread in soil and groundwater.End in diffusion End, the concentration of carbon in nutrient source is diluted to about 100ppm, for microorganism, becomes and jointly can absorb with chemical substance The concentration of degree.Therefore, the decomposition of chemical substance can be promoted.
Patent Document 3 discloses in order that the nutrient source after diluting fully can diffuse to underground and add nonionic The nutrient source of surfactant.Nutrient source herein comprises polyhydric alcohol and surfactant, and foregoing polyols are 62~68 weight Part selected from Sorbitol, mannitol, more than a kind of sugar alcohol of xylitol and the glycerol of 8~10 weight portions, aforementioned surfaces are lived Property agent is the nonionic surfactant of 1~5 weight portion, also comprises the water of 22~25 weight portions.
Prior art literature
Patent documentation
Patent documentation 1:Japanese Unexamined Patent Publication 2002-370085 publication (Japanese Patent Publication No. 3746726)
Patent documentation 2:Japanese Unexamined Patent Publication 2009-11939 publication (Japanese Patent Publication No. 5023850)
Patent documentation 3:Japanese Patent Publication No. 5587453
Content of the invention
Problems to be solved by the invention
The nutrient source (microorganism compositionss) with the composition of patent documentation 3 is actually applied, and has enumerated as made a reservation for Such effect.Such nutrient source is prepared in the factory in advance and is filled 18 liters of tanks (so-called " a pipeful of tank ":Hereinafter referred to as " transport container ") and it is transported to scene.The purification of soil needs the time of several weeks to several months, therefore to put into the transport of nutrient source Container great majority are for being placed on the situation of outdoor.
Then, create the problem that nutrient source solidifies in transport container, is difficult to take out from transport container.
For solution to problem
The present invention be in view of above-mentioned problem and expect, also will not coagulate in transport container even if providing and being placed on outdoor Solid microorganism with compositionss (nutrient source).
More specifically, the microorganism compositionss of the present invention are characterised by, described microorganism can purification soil, Organochlorine compound in lower water, described microorganism compositionss by
Sugar alcohol selected from any more than a kind in Sorbitol, mannitol;
Glycerol;
Nonionic surfactant;And
Water is constituted,
The containing ratio of aforementioned sugar alcohol is less than 6 times of aforementioned glycerol.
The effect of invention
The thermal shock even if the microorganism compositionss of the present invention are subject to repetition also will not solidify in transport container.Therefore, Transport to behind scene until use when manage on save worry.
Specific embodiment
Below the microorganism compositionss of the present invention are illustrated.Hereinafter illustrate exemplified with embodiments of the present invention and A part for embodiment, the invention is not restricted to following explanation.Purport without departing from the present invention is it is possible to following embodiment party Formula is changed.
The purpose of the microorganism compositionss of the present invention is, comprises for the microorganism in activating soil and subsoil water Material, so that it spreads from injection.Therefore, it is set to liquid and the low state of viscosity.In addition, for respect to soil and ground The purpose that microorganism in lower water is used with the state of highly diluted, needs for water solublity.In addition, it is net for soil and groundwater The purpose changed, needs to play the function of nutrient source.
As such material, can be suitably by the use of the Sorbitol in the sugar alcohol as polyhydric alcohol.But, equally Mannitol can be used.Sorbitol is illustrated herein.
In order that the Sorbitol being diluted with water keeps in soil and groundwater and mixes wetting agent.As moisturizing Agent, can be suitably by the use of the glycerol as 3 yuan of alcohol.This is because glycerol itself can become the nutrient source of microorganism.In addition, by In freezing point can be reduced in the same manner as ethylene glycol, therefore also there is the effect as anti-icing fluid.This is net in the low region of temperature It is useful for changing during soil and groundwater.
Even if in addition, also not solidifying in order under preserving in outdoor placement, for the microorganism combination before dilution Thing, contains glycerol with glycerol with respect to the ratio that Sorbitol is more than 1/6.Embodiment afterwards also would indicate that, as If the Sorbitol of polyhydric alcohol is placed with high concentrations more than 60 mass %, sometimes it is subject to the temperature change of surrounding, in transport Form crystal seed in container.And, sometimes centered on this crystal seed, produce crystallization and lead to solidify.
However, by the content reducing concentration or increase glycerol, it can be avoided that this phenomenon.Therefore, except Sorbitol Beyond the mixed proportion of glycerol, preferably the content of Sorbitol is adjusted to below more than 53 mass % and 58 mass %.
The microorganism compositionss of the present invention can also contain water with the ratio below 40 mass % degree.As basic Nutrient source is not need water.But, this is because it is also requisite that water is used for concentration regulation of nutrient source etc..Need Bright, water can also as Sorbitol, glycerol, other additive surplus.
In addition, the water being used preferably implements the water after sterilization treatment.This is because, contain fish moldss etc. in water miscellaneous Bacterium, Sorbitol also can become the nutrient source of these microorganisms, if therefore containing miscellaneous bacteria, causes microorganism to use during preserving The problem of compositionss corrosion.
In addition, sterilization treatment can also be for boiling process it is also possible to irradiation ultraviolet radiation etc..Alternatively, it is also possible to using pure water, This water initially not containing miscellaneous bacteria of ultra-pure water.
Nonionic surfactant is contained in nutrient source.When nutrient source is injected in soil and groundwater, surface Activating agent can reduce the surface energy of soil, is easily wetted soil with respect to nutrient source.As a result, along with capillary effect Really, nutrient source readily diffuses in soil and groundwater.Nonionic surfactant is unrelated with the pH of liquid and can play Surface activity.
Therefore, nonionic surfactant does not rely on the pH in soil and groundwater.In soil and groundwater Can be readily obtained anaerobic environment, therefore the anaerobic digestion aggravation of Organic substance and soil easily tends to acid.Even if in such ring Under border, as long as having nonionic surfactant it becomes possible to make microorganism compositionss spread.
As nonionic surfactant, it is possible to use:Polyoxyethylene alkyl ether, i.e. polyoxyethylene lauryl ether, poly- Oxygen ethylene cetyl ether, polyoxyethylene stearyl base ether, polyoxyethylene oleyl ether, polyoxyethylene higher alcohol ether, polyoxyethylene lima bean Cool base ether, the distyrenated phenyl ether of polyoxyethylene etc.;Sorbitan fatty acid ester, i.e. Span-20, Sorbitan monopalmitate, sorbitan monostearate, sorbitan monooleate, sorbitan distearyl Acid esters etc.;Polyoxyethylene sorbitan fatty acid ester, i.e. polyoxyethylene sorbitol acid anhydride list coconut fatty acid ester, polyoxyethylene Sorbitan laurate, polyoxyethylene sorbitan monopalmitate, polyoxyethylene sorbitan monostearate, Polyoxyethylene sorbitan tristearate anhydride, polyoxyethylene sorbitol acid anhydride three isostearate, polyoxyethylene sorbitol Acid anhydride monoleate, four Oleic acid polyoxyethylene sorbitol ethers etc..Wherein it is possible to suitably using polyoxyethylene lauryl ether.
And then, pH buffer can also be added in the microorganism compositionss of the present invention.PH buffer can be with respect to total Amount interpolation 1~4 weight portion.When adding pH buffer, suitably adjust the ratio with other compositions.
PH buffer can be suitably used as has lactic acid series buffer agent, citric acid system buffer agent, phosphate buffer agent, acetic acid It is buffer agent etc..They can add 1~4 weight portion.
Using as follows the reasons why pH buffer.As nutrient source microorganism compositionss by be injected into soil and ground In lower water, being capable of microorganism in activating soil and subsoil water.However, when the microorganism after activation causes anaerobic digestion aggravation, Generate the organic acid such as acetic acid, the pH in soil and groundwater reduces.If the pH of soil and groundwater excessively reduces, become to suppress The activity of microorganism.That is, when microorganism compositionss being injected in soil and groundwater, certain period after the implantation is formed Do not carry out the period of the decomposition of organochlorine compound etc..It is referred to as " lag phase of purification ".
PH buffer can somewhat relax the reduction of the pH that the generation of the organic acid such as acetic acid leads to, and can suppress pH Excessively reduce " lag phase of purification " leading to.Therefore, " lag phase of purification " disappears.As a result, there is soil and groundwater The advantage that period needed for purifying shortens.
Embodiment
The embodiment of the microorganism compositionss of the present invention is illustrated below.In order to confirm crystallization, prepare each shown in table 1 Sample, respectively fills 5 tanks in a transport container, applies temperature change in constant temperature test room.Transport container is common 18 liters of tanks, For iron.The process of protecting film or screening glass is not especially set in inwall.In constant temperature test room, little with 24 DEG C 12 When, at 15 DEG C the circulation of 12 hours apply thermal shock in 30 days.It should be noted that in temperature chamber, the change of temperature is with greater need for about 60 minutes.
Sample 1 is Sorbitol 65 mass %, glycerol 10 mass %, nonionic surfactant 2 mass %, water 23 matter Amount %.Nonionic surfactant uses polyoxyethylene lauryl ether.In addition, water is using the tap water through boiling.Thereafter All sample all sames.Crystallization is created for 5 tanks in sample 1,5 tank.Show the result in table 1.
Sample 2 is Sorbitol 60 mass %, glycerol 10 mass %, nonionic surfactant 2 mass %, water 28 matter Amount %.Crystallization is created for 5 tanks in sample 2,5 tank.Show the result in table 1.
Sample 3 is Sorbitol 59 mass %, glycerol 10 mass %, nonionic surfactant 2 mass %, water 29 matter Amount %.Crystallization is not all produced for sample 3,5 tank.Show the result in table 1.
Sample 4 is Sorbitol 58 mass %, glycerol 10 mass %, nonionic surfactant 2 mass %, water 30 matter Amount %.Crystallization is not all produced for sample 4,5 tank.Show the result in table 1.
Sample 5 is Sorbitol 55 mass %, glycerol 10 mass %, nonionic surfactant 2 mass %, water 33 matter Amount %.Show the result in table 1.Crystallization is not all produced for sample 5,5 tank.Show the result in table 1.
[table 1]
Test piece number (Test pc No.) 1 2 3 4 5
Sorbitol 65 60 59 58 55
Glycerol 10 10 10 10 10
Surfactant 2 2 2 2 2
Water 23 28 29 30 33
Result 5/5 5/5 0/5 0/5 0/5
The unit of the numeral of each sample is quality %
Result is to confirm the tank number of crystallization in 5 tanks
With reference to table 1, when Sorbitol is more than 59 mass %, in 5 tanks of each sample, more than half creates crystallization.So And, if 58 mass %, then there is not the tank producing crystallization in 5 tanks.As is well- known, the crystal of Sorbitol can lead to Cross and be once cooled to extremely low temperature and lentamente rise high-temperature to obtain.However, do not carry out such Temperature Treatment herein.
Accordingly, it is difficult to think the crystal producing Sorbitol purely thus it becomes crystal seed and crystallization occurs.Permissible Think the border of the liquid level of wall in transport container for the minute impurities being probably to be mixed into when preparing and microorganism compositionss Part is formed doubtful crystal seed and is produced crystallization with it as reason.The microorganism filled in transport container is combined herein The phenomenon of thing solidification is referred to as crystallization.
Then, it is 60 mass % and 58 mass % not causing crystallization for the Sorbitol causing crystallization, attempt The content changing glycerol.The composition of each sample is shown in table 2.
In sample 6, Sorbitol is 60 mass %, glycerol is 7 mass %, nonionic surfactant is 2 mass %, Water is 31 mass %.
In sample 7, Sorbitol is 58 mass %, glycerol is 7 mass %, nonionic surfactant is 2 mass %, Water is 33 mass %.
In sample 8, Sorbitol is 60 mass %, glycerol is 8 mass %, nonionic surfactant is 2 mass %, Water is 30 mass %.
In sample 9, Sorbitol is 58 mass %, glycerol is 8 mass %, nonionic surfactant is 2 mass %, Water is 32 mass %.
In sample 10, Sorbitol is 60 mass %, glycerol is 9 mass %, nonionic surfactant is 2 matter Amount %, water are 29 mass %.
In sample 11, Sorbitol is 58 mass %, glycerol is 9 mass %, nonionic surfactant is 2 matter Amount %, water are 31 mass %.
In sample 12, Sorbitol is 60 mass %, glycerol is 11 mass %, nonionic surfactant is 2 matter Amount %, water are 27 mass %.
In sample 13, Sorbitol is 58 mass %, glycerol is 11 mass %, nonionic surfactant is 2 matter Amount %, water are 29 mass %.
In sample 14, Sorbitol is 60 mass %, glycerol is 12 mass %, nonionic surfactant is 2 matter Amount %, water are 26 mass %.
In sample 15, Sorbitol is 58 mass %, glycerol is 12 mass %, nonionic surfactant is 2 matter Amount %, water are 28 mass %.
In sample 16, Sorbitol is 65 mass %, glycerol is 11 mass %, nonionic surfactant is 2 matter Amount %, water are 22 mass %.Show the result in table 2.
[table 2]
With reference to table 2, even thought sample 12 and 14 (Sorbitol 60 matter that produce crystallization by the result of table 1 Amount %), 5 tanks in 5 tanks all do not produce crystallization.In addition, for thinking sample 7, the 9,11 (mountain that should be unable to produce crystallization Pears sugar alcohol 58 mass %), 1 tank in 5 tanks or 2 tanks create crystallization.Even in addition, being judged as not producing the fortune of crystallization Defeated container, wherein also creates the block of fist size degree.
Can be drawn a conclusion by result above, the presence or absence of crystallization generation is not only relevant with the concentration of Sorbitol.In It is then to be conceived to the ratio of Sorbitol and glycerol.Table 2 shows that Sorbitol (is expressed as " S with respect to the ratio of glycerol: G”).
This Sorbitol is compared with respect to the ratio of glycerol, can predict and occur with 6 to 1 for boundary generation knot The situation of crystallization.Then, sample 16 is the content of the Sorbitol of sample 1 (Sorbitol is 65 mass %) shown in table 1, tastes Try the composition of the glycerol adding 11 mass %.In sample 16, Sorbitol is 5.9 to 1 with respect to glycerol.As shown in table 2, try In sample 16, even if Sorbitol is 65 mass %, as long as with respect to glycerol with less than 6 times of ratio, then 5 tanks in 5 tanks are not all Crystallization can occur.
As can seen above, if Sorbitol and the ratio of glycerol are less than 6 to 1 (if Sorbitol in microorganism compositionss Few), then it can be avoided that crystallization.
Because Sorbitol is closely similar with the structure of mannitol, therefore mannitol also creates same phenomenon. With regard to Sorbitol, based on the opinion obtaining in above-mentioned experiment with the composition hit and miss experiment of table 3 to determine whether crystallization.
Sample 17 is mannitol 60 mass %, glycerol 7 mass %, nonionic surfactant 2 mass %, water 31 matter Amount %.Mannitol (is expressed as " M in table 3 with the ratio of glycerol:G ") it is 8.5:1.
Sample 18 is mannitol 58 mass %, glycerol 9 mass %, nonionic surfactant 2 mass %, water 31 matter Amount %.Mannitol (is expressed as " M in table 3 with the ratio of glycerol:G ") it is 6.4:1.
Sample 19 is mannitol 60 mass %, glycerol 11 mass %, nonionic surfactant 2 mass %, water 27 Quality %.Mannitol (is expressed as " M in table 3 with the ratio of glycerol:G ") it is 5.4:1.
Sample 20 is mannitol 58 mass %, glycerol 11 mass %, nonionic surfactant 2 mass %, water 29 Quality %.Mannitol (is expressed as " M in table 3 with the ratio of glycerol:G ") it is 5.3:1.
Sample 21 is mannitol 65 mass %, glycerol 11 mass %, nonionic surfactant 2 mass %, water 22 Quality %.Mannitol (is expressed as " M in table 3 with the ratio of glycerol:G ") it is 5.9:1.
Show the result in table 3.With reference to table 3, mannitol is less than 6 with the ratio of glycerol:When 1, (mannitol is few or sweet Oil is many), do not produce crystallization.It should be noted that for sample 18, crystallization produces in 4 tanks in 5 tanks.Itself and Pyrusussuriensiss Sample 11 in the case of sugar alcohol is identical ratio of components, and in the case of Sorbitol, 1 tank in 5 tanks finds crystallization.Cause This, be that mannitol is more prone to crystallization than Sorbitol.
[table 3]
Test piece number (Test pc No.) 17 18 19 20 21
Mannitol 60 58 60 58 65
Glycerol 7 9 11 11 11
Surfactant 2 2 2 2 2
Water 31 31 27 29 22
Result 5/5 4/5 0/5 0/5 0/5
M∶G 8.5∶1 6.4∶1 5.4∶1 5.3∶1 5.9∶1
The unit of the numeral of each sample is quality %
Result is to confirm the tank number of crystallization in 5 tanks
The embodiment of the clean-up effect of soil of microorganism compositionss for confirm the present invention is illustrated below.Embodiment Carry out at the place polluted by tetrachloroethylene.Band water layer is 2.0~12.2m away from ground surface.In addition, four chloroethenes in subsoil water Alkene concentration is about 0.8mg/L.It is provided with the injection well of a diameter of 100mm in test, in well head connecting tube, carry out microorganism group The injection of compound.
In addition, in the local setting inspection well away from injection well 3m, termly carry out tce concentration in subsoil water, mountain Pears sugar alcohol concentration, the monitoring of pH.In addition, the injection well injecting each microorganism compositionss is set with inspection well with being adequately isolated Put, so that inspection well is not affected by each microorganism compositionss.
Each microorganism compositionss to be injected are using the aqueous solution being diluted to 2000ppm, continuous with 9.0L/ minute respectively After injection 7 days, simply continue to be monitored.
Embodiment 1 is by Sorbitol 52 mass %, glycerol 9 mass %, nonionic surfactant 2 mass % and water The mixture that 37 mass % mix.Sorbitol is " 5.7 with the ratio of glycerol:1”.It should be noted that as non-from Sub- property surfactant, using polyoxyethylene lauryl ether.Water uses the common boiling tap water boiling water of 10 minutes It is cooled to 25 DEG C of water.Composition and result are shown in table 4.
It should be noted that " G ratio " is " with respect to the ratio of glycerol " in table 4, glycerol is set to sugar alcohol when 1 by expression Ratio.In addition, " S " represents Sorbitol in table 4, " M " represents mannitol.
Embodiment 2 be by Sorbitol 55 mass %, glycerol 10 mass %, nonionic surfactant 2 mass % and The mixture that water 33 mass % mixes.Sorbitol is " 5.5 with the ratio of glycerol:1”.Embodiment 3 is by Sorbitol The mixture that 58 mass %, glycerol 10 mass %, nonionic surfactant 2 mass % and water 30 mass % mix. Sorbitol is " 5.8 with the ratio of glycerol:1”.
Embodiment 4 is by mannitol 52 mass %, glycerol 9 mass %, nonionic surfactant 2 mass % and water The mixture that 37 mass % mix.Mannitol is " 5.7 with the ratio of glycerol:1”.
Embodiment 5 is by mannitol 55 mass %, glycerol 10 mass %, nonionic surfactant 2 mass %, water The mixture that 33 mass % mix.Mannitol is " 5.5 with the ratio of glycerol:1”.Embodiment 6 is by mannitol 58 The mixture that quality %, glycerol 10 mass %, nonionic surfactant 2 mass % and water 30 mass % mix.Sweet Dew sugar alcohol is " 5.8 with the ratio of glycerol:1”.
The sugar alcohol of the microbial composite of all of embodiment is 6 with respect to glycerol:Less than 1 ratio (sugar alcohol is few). Composition and result are shown in table 4.It should be noted that when carrying out this embodiment, for the micro- life being filled into transport container The thing longer situation of compositionss is to carry out outdoor placement more than 1 month in test site, but 1 tank does not all occur crystallization.
[table 4]
With reference to table 4, resolution ratio is obtained by the concentration and the concentration after 30 days of the tetrachloroethylene before testing, is represented with %.Separately Outward, the concentration (mg/L) of the sugar behind 7 days at the sampling spot away from well 3m is shown.
In embodiment 1~6, the tetrachloroethylene at place away from well 3m has all decomposed more than 95%.In addition, taking away from well 3m The concentration of the sugar after 7 days at sample place is more than 800mg/L.It follows that the composition of the microorganism compositionss of the present invention with The state of highly diluted improves the wettability of soil surface, while being diffused into underground, contributes to the decomposition of tetrachloroethylene.
Industrial applicability
The microorganism compositionss of the present invention as using the microorganism in soil and groundwater by soil and groundwater Organochlorine compound decompose, purify when nutrient source and suitably use.

Claims (2)

1. a kind of microorganism compositionss are it is characterised in that described microorganism being capable of purification soil, the organic chloride in subsoil water Compound, described microorganism compositionss by
Sugar alcohol selected from any more than a kind in Sorbitol, mannitol;
Glycerol;
Nonionic surfactant;And
Water is constituted,
The containing ratio of described sugar alcohol is less than 6 times of described glycerol,
Described sugar alcohol is below more than 53 mass % and 58 mass % in described microorganism compositionss.
2. microorganism compositionss according to claim 1 are it is characterised in that described nonionic surfactant is poly- Oxygen ethylene lauryl ether.
CN201580003186.9A 2015-04-24 2015-04-24 Microorganism compositionss Active CN105960446B (en)

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
PCT/JP2015/002248 WO2016170562A1 (en) 2015-04-24 2015-04-24 Composition for microorganisms

Publications (2)

Publication Number Publication Date
CN105960446A CN105960446A (en) 2016-09-21
CN105960446B true CN105960446B (en) 2017-03-01

Family

ID=55347030

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201580003186.9A Active CN105960446B (en) 2015-04-24 2015-04-24 Microorganism compositionss

Country Status (4)

Country Link
JP (1) JP5866508B1 (en)
CN (1) CN105960446B (en)
MY (2) MY161710A (en)
WO (1) WO2016170562A1 (en)

Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101890211A (en) * 2009-05-21 2010-11-24 环保股份有限公司 Additive for purifying a medium contaminated by a mineral oil and purification method
JP5587453B1 (en) * 2013-03-29 2014-09-10 パナソニック株式会社 Microbial composition

Family Cites Families (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP3746726B2 (en) * 2001-04-13 2006-02-15 松下電器産業株式会社 Methods for reducing nitrate nitrogen and volatile organic compounds in soil and groundwater
JP2007083169A (en) * 2005-09-22 2007-04-05 Miyoshi Oil & Fat Co Ltd Decontaminating agent for soil and ground water
JP5023850B2 (en) * 2007-07-05 2012-09-12 パナソニック株式会社 Method for purifying contaminated soil and groundwater
JP6195148B2 (en) * 2013-03-28 2017-09-13 パナソニックIpマネジメント株式会社 Microbial nutrient source injection device

Patent Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101890211A (en) * 2009-05-21 2010-11-24 环保股份有限公司 Additive for purifying a medium contaminated by a mineral oil and purification method
JP5587453B1 (en) * 2013-03-29 2014-09-10 パナソニック株式会社 Microbial composition

Also Published As

Publication number Publication date
WO2016170562A1 (en) 2016-10-27
MY162881A (en) 2017-07-20
CN105960446A (en) 2016-09-21
MY161710A (en) 2017-05-15
JPWO2016170562A1 (en) 2017-04-27
JP5866508B1 (en) 2016-02-17

Similar Documents

Publication Publication Date Title
CN105087538B (en) A kind of oil degradation microbial inoculum and its preparation method and application
US7030287B2 (en) Method of decreasing nitrate nitrogen and volatile organic compound in soil and groundwater
Gibb et al. Bioremediation kinetics of crude oil at 5 C
JP3746726B2 (en) Methods for reducing nitrate nitrogen and volatile organic compounds in soil and groundwater
US6679992B1 (en) Method and apparatus for purifying polluted substances containing halogenated organic compound
CN104086065B (en) Oil and gas well drilling operation discarded slurry micro-organism treatment process
CN1173835A (en) Anaerobic/aerobic decontamination of DDT contaminated soil by repeated anaerobic/aerobic treatments
CN105960446B (en) Microorganism compositionss
CN109534517A (en) Prosparol and its preparation method and application
JP2007268401A (en) In-situ cleaning method and in-situ cleaning system of contaminated soil and/or ground water
CN104843865A (en) Liquid carbon source material for in-situ remediation of groundwater nitrate and Cr<6+> pollution
CN108636356A (en) A kind of cornstalk biological charcoal and restorative procedure that can repair nitrogen phosphorus pollution of area source
JP5481846B2 (en) Method for purifying contaminated soil or groundwater
TWI524914B (en) Composition for microbiological use
JP5587453B1 (en) Microbial composition
CN105617856A (en) Biological absorbent for treating hydrocarbon organic waste gas and preparation method thereof
CN205856279U (en) One is volatile organic matter segregation apparatus be applicable to Treated sewage reusing
JP2005305321A (en) Contamination purification method
RU2528198C1 (en) Method for detoxification of soil contaminated with oil and oil products
Zhang et al. The driving effects of nitrogen deposition on nitrous oxide and associated gene abundances at two water table levels in an alpine peatland
CN105940098B (en) Microorganism composition
Tindall et al. Part 1: Vadose-zone column studies of toluene (enhanced bioremediation) in a shallow unconfined aquifer
JP6212842B2 (en) Purification method for contaminated soil
KR100974143B1 (en) In situ biodegradation enhancement method in the contaminated subsurface using microbubble suspension, and the microbubble suspension
JP2004188406A (en) Anaerobic purifying method for soil

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
GR01 Patent grant
GR01 Patent grant