CN105521989B - Restoration of the ecosystem composition and the ecological restoring method for utilizing this - Google Patents
Restoration of the ecosystem composition and the ecological restoring method for utilizing this Download PDFInfo
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- CN105521989B CN105521989B CN201510147418.XA CN201510147418A CN105521989B CN 105521989 B CN105521989 B CN 105521989B CN 201510147418 A CN201510147418 A CN 201510147418A CN 105521989 B CN105521989 B CN 105521989B
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B09—DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
- B09C—RECLAMATION OF CONTAMINATED SOIL
- B09C1/00—Reclamation of contaminated soil
- B09C1/10—Reclamation of contaminated soil microbiologically, biologically or by using enzymes
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B09—DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
- B09C—RECLAMATION OF CONTAMINATED SOIL
- B09C1/00—Reclamation of contaminated soil
- B09C1/08—Reclamation of contaminated soil chemically
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B09—DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
- B09C—RECLAMATION OF CONTAMINATED SOIL
- B09C1/00—Reclamation of contaminated soil
- B09C1/10—Reclamation of contaminated soil microbiologically, biologically or by using enzymes
- B09C1/105—Reclamation of contaminated soil microbiologically, biologically or by using enzymes using fungi or plants
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- 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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- C12—BIOCHEMISTRY; BEER; SPIRITS; WINE; VINEGAR; MICROBIOLOGY; ENZYMOLOGY; MUTATION OR GENETIC ENGINEERING
- C12N—MICROORGANISMS OR ENZYMES; COMPOSITIONS THEREOF; PROPAGATING, PRESERVING, OR MAINTAINING MICROORGANISMS; MUTATION OR GENETIC ENGINEERING; CULTURE MEDIA
- C12N1/00—Microorganisms, e.g. protozoa; Compositions thereof; Processes of propagating, maintaining or preserving microorganisms or compositions thereof; Processes of preparing or isolating a composition containing a microorganism; Culture media therefor
- C12N1/12—Unicellular algae; Culture media therefor
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Abstract
It include algae, the culture medium of the algae, the barren land restoration of the ecosystem composition of soil fixing agent and super water-absorbent material and the barren land ecological restoring method using this present invention relates to one kind.The present invention can prevent desertification and yellow sand, waste coal mine and oil pollution are modified to the ecological environment for being suitable for plant growth to form Biological Soil Crusts in the short time, can prevent from causing ecology and environmental pollution by desert, waste coal mine and oil pollution.
Description
Technical field
The present invention relates to restoration of the ecosystem composition and using this ecological restoring method, more particularly to manufacturing one kind can be
The restoration of the ecosystem composition of Biological Soil Crusts is effectively formed on barren land soil in short time, this be introduced into it is barren it
The ecological environment of Cheng Kerang plant growth is repaired ecological environment on ground.
Background technique
Biological Soil Crusts (biological soil crusts, BSCs), which are that Arid Area soil surface is common, inhabites
Ground type, it is reported that playing critical function in terms of ecology.The Biological Soil Crusts by cyanobacteria (cyanobacteria),
Green algae (green algae), lichens (lichen), mosses (mosses), actinomyces (actinomyces), filamentous fungi
The substance of microorganisms such as (filamentous fungi) and their secretions shape in conjunction with organic substance and soil lining in soil
At.The conjunctiva (crust) formed by microorganism can prevent the erosion of wind or water to soil, and carbon and nitrogen is fixed in the soil,
It helps soil to maintain stability, avoid the soil erosion, the moisture content in maintenance soil, plant growing cycle, gives the ecosystem
Reparation generate and many influence (St.Clair, L.L., et al., 1986, Recjam.Reveg.Res., 4,261-269.;
Greene R.S.B.,et al.,1990,Aust J.Soil Res.,25,775-777.;Johanse,J.R.,et al.,
1993,Great Basin Nat.,53,73-88.;Eldridge,D.J.and Bradstock,R.A.,1994,
Cunninghamia,3,521-527.;Eldridge,D.J.and Greene,R.S.B.,1994,Aust J.Soil Res.,
389-415.)。
In particular, the skinning formed by cyanobacteria and mosses, due to secreting sticky polysaccharide protection knot in cell peripheral
Film (sheaths), facilitates in conjunction with soil particle in coagulating soil.In addition, the root of lichens and mosses and soil grain
Son combines, and improves soil to the erosion resistance of wind and water.
Recently, the parties concerned are studied, it is intended to promote Biological Soil Crusts (BSCs) using mosses and cyanobacteria
It is formed, during the final ecological system degradation shortened after environment is destroyed.As its concrete example, Chen et al. (Chen,
L.Z.et al., 2006, Journal of Arid.Environments 67,521-527.) disclose a kind of technology, Xiang Zhong
Micro- sheath algae (Microcoleus is inoculated on the sand dune of the reduction in the state Inner Mongol (Inner mongolia, China)
Vaginatus), the artificial algae conjunctiva in desert is formed;Wang et al. (Wang, W.B., et al., 2009, Soil Biology
And Biochenmistry 41,926-929.) a kind of technology is disclosed, in desert area, straw checkerboard barrier (straw is set
Checkborard) and Self-watering is to irrigate (automatic sprinkling micro-irrigation) system, Xiang Qi
It is inoculated with cyanobacteria rehabilitating soil;Xiao et al. (Xiao, B., et al., 2011, Applied Soil Ecology, 48,11-
17.) open, the loess plateau (loess plateau) of Xiang Zhongguo is inoculated with the Biological Soil Crusts formed by mosses (moss), into
Pedestrian's work proliferation results, the proliferation of Biological Soil Crusts permeated, rainwash (overland flow), run-off
(runoff) and the influence of water re-supplied.In addition, Malam Issa et al. (Malam Issa, O., et al., 2007,
Plant Soil, 290,209-219.) show that the quality on the physical layer of soil, Yu can be improved in the inoculation of cyanobacteria
And He (Yu, H.and Y.He., 2011, Int.Conf.Bioinformatics Biomedical Eng., 1-3.) shows indigo plant
The polysaccharide of algae bacterial secretory plays an important role to the stability of soil, and Wu et al. (Wu, Y., et al., 2013, Plant
Soil, 370,115-124.) show that the conjunctiva of cyanobacteria formation can improve the fertility and microenvironment of soil.On but
Biomass of the leading document to the cyanobacteria being inoculated in artificial bio-membrane's soil crust (BSCs) forming process is stated, is effectively cultivated
Method etc., is not still stated clearly, in terms of area in large scale forms artificial bio-membrane's soil crust (BSCs), there is also
The problem of cultivating a large amount of cyanobacterias.
Existing desert or just in the area of desertification, in order in the Zinc fractions Biological Soil Crusts of such kind of area
(BSCs), a kind of straw checkerboard barrier system (straw checkerboard system) for being inoculated with the microorganisms such as cyanobacteria is developed.
The method, which had in the short time, stabilizes the sand dune of adverse environment condition, effectively puts aside the organic matter and nutritional ingredient of soil
The advantages of (Li, X.R., et al., 2006, Ecological Engineering, 28,149-157.).But the straw checkerboard barrier system
System is not only difficult to be formed uniformly Biological Soil Crusts, but also it is long to form the time, then 2~3 years short, it is long then 5~7 years.And this
The also non-mechanization of method then needs many manpowers if applicable in sweeping area, repairs certain above scale and destroys soil
When, there is very big expense burden.
For this purpose, related research attempt to develop it is a kind of with the effect while be economically applicable to extensive area
Method, while the microorganism that can form Biological Soil Crusts is fixed on sand bed surface at the beginning, with moisture or nutrition at
The soil fixing agent that point aspect can promote microorganism growth is handled, repair ecological environment (Liu, J., et al., 2012,
Environ Earth Sci.,65,589-595.;Corti,A.,et al.,2002,Macromolecular Chemistry
and Physics,203,1526-1531.;Yang,J.,et al.,2007,Environmental Pollution,149,
125-130.).The soil fixing agent improves the stability of sand, prevents because of wind or rainfall, desert or just in the dry of desertification
It is mobile that dry and regional partial desiccation sand is detached from barren land.When using the soil fixing agent, with without using the case where compared with,
The intensity of the Biological Soil Crusts formed in barren land, moisture storage capacity etc. are improved in the future, it is easier to barren
Ground soil restoration of the ecosystem.But the soil fixing agent is by sad fungi or the Biodegradable substance structure of bacterial decomposition
At, and while being exposed to intensive ultraviolet and the violent temperature difference, decomposes, and soil stabilization function gradually dies down, and comes from long-term angle
It sees low efficiency, the biomass to form the microorganism of Biological Soil Crusts can be reduced, there are problems.
And it is let out by oil storages facilities such as extensive oil storage setting, petroleum pipeline, gas stations through the oils between several years or even many decades
Leak cause contaminated soil, or by coal mine cinder contaminated soil and waste coal mine soil due to moisture it is very insufficient, cause
Plant stops growing, the also secondary pollutions such as initiation underground water pollution.
The environmental hazard that the soil ecosystem and human body caused with soil pollution is subjected to is of increasing concern, U.S. etc.
Developed country in exploitation, be applicable in restorative procedure and physics, chemical repair method biologically.But these methods, by causing
The reason of soil pollution, the scope of application are limited, and repair certain scale more than soil when, expense burden it is quite big.
To each inventor of the invention, in order to develop one kind not by regional feature, such as desert area or Polluted Soil territory
The limitation in area, it is unrelated with pollution cause, it comprehensive can be applicable in, it can life that is rapid, being stably formed Biological Soil Crusts (BSCs)
State reparation composition and make great efforts as a result, completing the present invention.
Summary of the invention
(1) technical problems to be solved
It include algae, the culture medium of the algae, soil fixing agent and superabsorbent water the purpose of the present invention is to provide one kind
The barren land restoration of the ecosystem composition of material.
Another object of the present invention is to provide a kind of barren land soil remediation methods, and the restoration of the ecosystem is combined
Object be introduced into desert, waste coal mine, oil pollution, volcano lacquer putty, toxic mineral or trade waste discard place, rock and
The barren lands such as bald mountain form Biological Soil Crusts, repair the soil of barren land in the short time.
(2) technical solution
The present invention provides a kind of barren land restoration of the ecosystem composition comprising algae, the culture medium of the algae, soil
Earth fixative and super water-absorbent material.
In the present invention, " algae " forms Biological Soil Crusts in the soil surface of barren land, it means that lichens
Parasymbiosis algae and cyanobacteria (cyanobacteria).
In the present invention, " culture medium " is the training for being commonly used for culture lichens symbiotic algae or cyanobacteria
Base is supported, for example, lichens symbiotic algae is BBM culture solution, cyanobacteria is BG-11 culture solution.
" the lichens symbiotic algae " constitutes a part of lichens and its thallus (thallus), and leaf can be passed through by referring to
Green element carries out photosynthetic green algae or blue algae.
" lichens " refers to form the fungi of lichens (fungi) and algae (algae) and/or cyanobacteria
(cyanobacteria) symbiosis complex.
" thallus (thallus) " is true by lichens symbiotic algae or the cell of cyanobacteria, and formation lichens
The mycelia of bacterium is constituted, and is sorodium (soredium), isidium (isidia) or (vegetative that nourishes and generates
Propagation the trophosome (trophozoite) of lichens needed for).
Lichens symbiotic algae of the invention includes but is not limited to asymmetric ball algae (Trebouxia altogether
Asymmetrica), green alga (Trebouxia impressa: transliteration, original text word can not investigate), jamesii are total to ball algae
(Trebouxia jamesii: transliteration, original text word can not investigate), usneae are total to ball algae (Trebouxia usneae: sound
Translate, original text word can not investigate), Magna is total to ball algae and is total to ball algae (Trebouxia magna: transliteration, original text word can not be examined
Card), erici is total to ball algae (Trebouxia erici: transliteration, original text word can not investigate), corticola is total to ball algae
(Trebouxia corticola: transliteration, original text word can not investigate) etc. belongs to altogether ball algae (Trebouxia), the total ball algae of puppet
(Pseudotrebouxia) belong to, multiple coccidia splits algae (Stichococcus diplosphaera) etc. and splits an algae
(Stichococcus) belong to, fir orange algae (Trentepohlia abietina), verdigris orange algae (Trentepohlia
Aeruginosa), aurea orange algae (Trentepohlia aurea: transliteration, original text word can not investigate), teju orange algae
The oranges algae such as (Trentepohlia arborum) (Trentepohlia) category etc..
" cyanobacteria " of the invention constitutes a part of lichens and thallus, refers to and aquatic does photosynthesis
Bacterium.Specifically comprising Nostoc commune (Nostoc commune), yellowish pink nostoc (Nostoc carneum), hair-like
The nostocs (Nostoc) such as nostoc (Nostoc flagelliforme Born et Flsh) belong to, crytovainatus sheath silk
The sheaths silk algaes (Lyngbya) such as algae (Lyngbya crytovainatus Schk: transliteration, original text word can not investigate) belong to, and have sheath
Micro- sheath algae (Microcoleus) such as micro- sheath algae (Microcoleus Vaginatus (Vauch) Gom) belongs to, anabena
(Anabaena) belong to, the chroococcoids (Chrococcus) such as chroococcoid that grows nonparasitically upon another plant (Chrococcus epiphyticus) belong to, and stick ball algae
(Gloecapsa) belong to, the seats algae (Phormidium) such as Phormidium tenue (Phormidium tenue) belongs to, and red lid sesame becomes discrimination algae
(Scytonema japonicum) etc. becomes discrimination algae (Scytonema) and belongs to, pevalekii cytoalgae (Synechocystis
Pevalekii: transliteration, original text word can not investigate) etc. cytoalgaes (Synechocystis) belong to, eyebrow algae (Calothrix) belong to,
Single discrimination algae (Tolypothrix) category etc..
In the present invention, the algae is relative to 100 parts by weight of culture medium, with 10 to 20 parts by weight, preferably with 15 to 17
The mixing of parts by weight content is advisable.When the algae content is less than 10 parts by weight, the Zinc fractions Biological Soil Crusts of barren land
Required time is long, when algae content exceeds 20 parts by weight, compared with the case where being inoculated with its following content, and barren land soil grain
The increase very little of sub- stability and the cell caking property polysaccharide content in conjunction with the organic substance of soil reduces efficiency.
In the present invention, the soil fixing agent includes hydrophily colloid (colloid) particle, the colloidal particle be extraction in
The hydrophily colloidal particle of plant or vegetable seeds is advisable.The hydrophily colloidal particle is reacted with water, is occurred gelatinization (gel),
The caking property for improving soil, can prevent the environmental factors such as heavy rain or wind from leading to soil losses.
The plant or vegetable seeds are plant or the vegetable seeds for not influencing algal grown, can make xylophyta, grass
This class plant, plant exotic species (plant exotic species) or their mixed plant (Mixed Plants).As
An example, can be Asiatic plantain (asian plantain) seed, Euphorbiaceae (Euphorbiaceae) vegetable seeds, soybean etc., most
It is Chinese herbaceous peony grass seed well.
Soil fixing agent of the invention can also include answering needed for plant growth other than colloidal particle containing hydrophily
Hefei material, hydrolysis of urea inhibitor, nitridation inhibitor, anionic polymerization body, water etc..The compound fertilizer is rapid using fertilizer efficiency
Quick action fertilizer is advisable, and the quick action fertilizer can be the organic matters such as mixing bark, sawdust, pig manure, chicken manure, lime, manganese, oxygen
Change the fertilizer of the mineral such as iron, nitrogen, phosphoric acid, calcium.The hydrolysis of urea inhibitor, as long as the ammonia of nitrogen component can be inhibited,
It can be used, than if any PPD (phenyl phosphorodiamidate: phenyl phosphorus diamides) and NBPT (N-butyl
Thiophosphoric triamide: N-(n-butyl) thiophosphoric triamide).The nitridation inhibitor, as long as nitrous can be inhibited
Change acts on (nitrozation) and can be used, than if any N-Serve (N-serve), TU, dicyandiamidines (guanyl urea), ammonium phosphate
Magnesium (magnesium ammonium phosphate), GUP (guanyl phosphate: phosphoric acid amidino groups), GUS (guanyl
Sulfate: base sulfuric acid), triazine (triazine) etc..As long as the anion condensate can be with electricity chemosphere face handle
Fertilizer component is incorporated in micro- soil, prevents soil loss, that is, arbitrary substance can be used, than if any acrylic copolymer
(acrylic copolymer), from copolymer derived from crotonic acid (crotonic acid), from maleic acid (maleic
Acid), fumaric acid (fumaric acid), itaconic acid (itaconic acid), acid anhydrides (anhydride), alicyclic vinyl
(Vinyl ester), vinethene (vinyl ether), vinyl halide (Vinyl halogenide halide), phenyl
Polymer derived from ethylene (Phenyl vinyl) derivative, acrylic acid (acrylic acid) and its ester (ester), methyl-prop
The copolymer of olefin(e) acid (methacrylic acid) and methyl methacrylate (methyl Methacrylate), metering system
The copolymer etc. of acid and ethyl acrylate (ethyl acrylate).
As concrete example, the present invention be can be used containing extraction in the hydrophily colloidal particle of semen plantaginis seed, and anion is poly-
Close object, the trade name TKS7 of compound fertilizer and water (Seven treasuries bio industries company's:STBi,
Korea)。
In the present invention, the soil fixing agent is relative to 100 parts by weight of culture medium, with 0.5 to 1.5 parts by weight content, most
It is to be advisable with the mixing of 0.9 to 1.1 parts by weight content well.If the soil fixing agent content is less than 0.5 parts by weight, with algae
When being suitable for barren land soil together, cell contact polysaccharide (EPS) content in barren land soil increases few, exposure
It when natural environment, is easy to be corroded by wind or rain, if soil fixing agent content exceeds 1.5 parts by weight, and contains its following content
The case where compare, the barren land soil aggregation intensity that is applicable in and effect very little, efficiency are increased to the resistance of natural environment
It is bad.
In the present invention, the super water-absorbent material is the substance for promoting algal grown, for example be can be used from pitch cream
The mixture of liquid (asphalt emulsion), gypsum powder and Sodium Polyacrylate (sodium polyacrylate) etc., more preferably
It is the mixture of Sodium Polyacrylate, humic acid (humic acid), minerals etc., preferably Sodium Polyacrylate.
In the present invention, the super water-absorbent material is best with 0.05 to 0.15 parts by weight relative to 100 parts by weight of culture medium
It is to be advisable with the mixing of 0.09 to 0.11 parts by weight content.If the content of the super water-absorbent material is given birth to less than 0.05 parts by weight
The formation overlong time of object soil crust (BSCs), if the content of super water-absorbent material exceed 0.15 parts by weight, with contain one
The case where lower content, is compared, and the barren land soil aggregation intensity that is applicable in and increases effect very to the resistance of natural environment
Small, efficiency is bad.
Barren land restoration of the ecosystem composition of the invention and independent inoculation algae or the super water-absorbent material of access and soil
The case where fixed agent composition, is compared, and the stability reunion and algae bio amount of soil improve, and can be effectively formed in a short time
Biological Soil Crusts can provide the soil of plant growth for barren land.
In the present invention, the barren land refer to desert, waste coal mine, oil pollution, volcano lacquer putty, toxic mineral or work
Industry waste discard place, rock and the medium moss liverwort (moss) of bald mountain, cryptogam (spore-producing
Plant), gymnosperm (gymnosperm), flowering plant (flowering plant), monocotyledon
(monocotyledon), the place that dicotyledon (dicotyl) can not grow and breed.
It includes algae that the present invention, which provides a kind of introduce, the culture medium of the algae, soil fixing agent and super water-absorbent material
The barren land ecological restoring method that restoration of the ecosystem composition is realized.
Algae contained by the barren land restoration of the ecosystem composition being applicable in barren land ecological restoring method of the invention
The contents such as class, type, content, the effect of culture medium, soil fixing agent and super water-absorbent material are identical as foregoing teachings, omitted below
It is described in detail.
In the present invention, the barren land restoration of the ecosystem composition and algae or mixed soil fixative and super water-absorption material
The chemicals of material is compared, and the increased effect of biomass of stability reunion and algae with barren land soil is introduced into
When barren land soil, 30 to 90 days from introduction, after especially 45 to 75, the effect for forming Biological Soil Crusts is presented.
In the present invention, the introduction refers to: at barren land surface or position from surface 1cm depth, inoculation include algae,
The barren land restoration of the ecosystem composition of soil fixing agent and super water-absorbent material.Here, the inoculation, with the total face of barren land
Product (such as: 1m2) subject to, allow the ratio of restoration of the ecosystem composition to account for 20% or more, more preferably 30%, more preferably 40%, most
It is well 50% or more, inoculation method is to broadcast sowing restoration of the ecosystem composition to barren land.
In a concrete example, respectively being put into soil fixing agent 1g (10g/m to BG-11 fluid nutrient medium2) and superabsorbent water
Material 0.1g (1g/m2) dissolved after, be put into algae 16g (160g/m2), the composition that uniformly mixing manufactures, to BG-11 liquid
Body culture medium is put into soil fixing agent 1g (10g/m2) and super water-absorbent material 0.1g (1g/m2) preparation and the algae of manufacture are mixed afterwards
16g(160g/m2) be inoculated into desert soil, whether observation Biological Soil Crusts formation as a result, after 2 months, be inoculated with algae
Barren land soil initially forms Biological Soil Crusts, and be inoculated with restoration of the ecosystem of the invention with composition (soil fixing agent+
Super water-absorbent material+algae) desert soil compared with the case where being only inoculated with algae, form much more significant Biological Soil Crusts
(reference implementation example 3 and Fig. 1).
(3) beneficial effect
Barren land restoration of the ecosystem composition of the invention can increase the biomass and EPS content of algae, to heavy rain
And other have good durability, the stability reunion of soil can be improved with the environmental attack of water, it is barren when being introduced into
Ground soil when, have the effect of being effectively formed Biological Soil Crusts in the short time (30 to 90).To described barren
Ground restoration of the ecosystem when being introduced into barren land soil with composition, desertification and yellow sand can be prevented, can be waste coal mine and oil
Class is impurely equal to be impurely modified to the ecological environment for being suitable for plant growth.Meanwhile it can prevent by desert, waste coal mine and oil
The ecology and environmental pollution that class impurely causes.
Detailed description of the invention
Fig. 1-Fig. 8 is respectively being put into soil fixing agent 1g (10g/m to BG-11 fluid nutrient medium2) and super water-absorbent material
0.1g(1g/m2) dissolved after, be put into algae 16g (160g/m2), uniformly mixing manufacture composition, to BG-11 liquid train
Feeding base is put into soil fixing agent 1g (10g/m2) and super water-absorbent material 0.1g (1g/m2) preparation and algae 16g of manufacture are mixed afterwards
(160g/m2) it is inoculated into desert soil, result schematic diagram whether observation Biological Soil Crusts are formed.Wherein,
Fig. 1 is the schematic diagram of the control group after just inoculation;
Fig. 2 is the schematic diagram of the algae after just inoculation;
Fig. 3 is soil fixing agent+super water-absorbent material+algae schematic diagram after just inoculation;
Fig. 4 is soil fixing agent+super water-absorbent material schematic diagram after just inoculation;
Fig. 5 is the schematic diagram of the control group of inoculation after two months;
Fig. 6 is the schematic diagram of the algae of inoculation after two months;
Fig. 7 is the soil fixing agent+super water-absorbent material+algae schematic diagram of inoculation after two months;
Fig. 8 is the soil fixing agent+super water-absorbent material schematic diagram of inoculation after two months;
The desert soil of inoculation distilled water has been used as control group.
Specific embodiment
In order to make the object, technical scheme and advantages of the embodiment of the invention clearer, below in conjunction with the embodiment of the present invention
In attached drawing, the technical scheme in the embodiment of the invention is clearly and completely described, it is clear that described embodiment is
A part of the embodiment of the present invention, instead of all the embodiments.Based on the embodiments of the present invention, those of ordinary skill in the art
Every other embodiment obtained without creative efforts, shall fall within the protection scope of the present invention.
Embodiment 1: prepare super water-absorbent material (superabsorbent, SAP)
As super water-absorbent material, Sodium Polyacrylate (sodium polyacrylate) powder is prepared.
Embodiment 2: prepare soil fixing agent
Hydrophily the colloidal particle 25g, anionic polymerization object 180g and compound fertilizer 100g extracted from semen plantaginis seed
It is put into 4L water and dissolves, be prepared for soil fixing agent.
Comparative example 1: know the preparation for mixing super water-absorbent material and soil fixing agent
The super water-absorbent material 0.1g (1g/m that the embodiment 1 is manufactured2) and the embodiment 2 manufacture soil fixing agent
1g(10g/m2) be put into BG-11 fluid nutrient medium (BOSUNG SCIENTIFIC Co., Ltd, Korea) 100mL, it mixes
It is prepared for preparation.
Embodiment 3: it is formed using the Biological Soil Crusts of algae, super water-absorbent material and soil fixing agent
3-1. prepares algae
The soil acquired from 2012 in Ningxia, China is inoculated into 100cm after separation dry tolerance algae (Nostoc sp.)
(cross) × 50cm (perpendicular) × 30cm (height) size clear acrylic (acrylic) cultivates sink, after culture one month, centrifugation point
From only collecting sediment.In the lower part of culture sink, water flow electrode is installed, allows culture solution Uniform Flow, in the fixed air in center
Feeding mechanism, supply air.Culture medium is BG-11 (BOSUNG SCIENTIFIC Co., Ltd, Korea), it is contemplated that non-fully
The mass propgation liquid of sealing structure and 100L or more are difficult to accomplish that sterilization uses, and pass through precipitating filter core, blue carbon filter core, white carbon filter core
It is used after carrying out purification and degerming to tap water.Maintain 30 DEG C of temperature, light 12000lux condition culture medium (PGW 36,
Conviron, Canada) in cultivated, night condition is 25 DEG C of temperature, light 0lux, and the photoperiod is set as 12 hours.
Composition 3-2. of the invention prepares
The super water-absorbent material 0.1g (1g/m that the embodiment 1 prepares is put into BG-11 fluid nutrient medium 100mL2) and institute
State the soil fixing agent 1g (10g/m of the preparation of embodiment 22) the algae 16g (160g/ of the embodiment 3-1 culture is put into after mixing
m2), uniformly mixing, manufactured composition of the invention.
3-3. China, (Shapotou, Ningxia) desert test garden scene, Shapotou is applicable in
In Chinese Shapotou desert, with the height inside and outside 10~30cm, grid frame, manufacture is arranged in the cubic interval 1m
Test garden.Later, the present composition embodiment 3-2 prepared, the preparation and BG-11 liquid that the comparative example 1 prepares
Algae 16g (the 160g/m that body culture medium 100mL is cultivated containing the embodiment 3-12) fluid nutrient medium, respectively with 1L, uniformly
The mode for soaking test garden surface is inoculated with, whether the formation of Biological Soil Crusts is observed after 2 months.It is used as control group
It is inoculated with the desert soil of distilled water.Its result is as shown in Figure 1.
Test result after inoculation 2 months, is inoculated with the desert soil of control group and is inoculated with the desert of the preparation of comparative example 1
The not formed Biological Soil Crusts of soil.On the contrary, although the desert soil of inoculation algae initially forms Biological Soil Crusts, but it is inoculated with
The desert soil of the algae of super water-absorbent material and soil fixing agent is mixed with compared with the desert soil for being only inoculated with algae, is formd
The Biological Soil Crusts of significant volume.
Claims (7)
1. a kind of barren land restoration of the ecosystem composition, it is characterised in that: the composition includes the training of algae, the algae
Support base, soil fixing agent and super water-absorbent material;In the composition, 100 parts by weight of culture medium of the algae, the algae
10 to 20 parts by weight, 0.5 to 1.5 parts by weight of soil fixing agent, super 0.05 to 0.15 parts by weight of water-absorbent material;It is described
Soil fixing agent includes extracting the hydrophily colloidal particle in semen plantaginis seed, anionic polymerization object and compound fertilizer;It is described super
Water-absorbent material is the one kind or two or more mixture in asphalt emulsion, gypsum powder and Sodium Polyacrylate.
2. barren land restoration of the ecosystem composition according to claim 1, it is characterised in that:
The algae is one or more of lichens symbiotic algae and cyanobacteria.
3. barren land restoration of the ecosystem composition according to claim 2, it is characterised in that:
The lichens symbiotic algae be belong to total ball algae (Trebouxia) belongs to, pseudo- ball algae (Pseudotrebouxia) altogether belongs to,
Split one kind that an algae (Stichococcus) belongs to and orange algae (Trentepohlia) belongs to.
4. barren land restoration of the ecosystem composition according to claim 2, it is characterised in that:
The cyanobacteria is to belong to nostoc (Nostoc) category, sheath silk algae (Lyngbya) category, micro- sheath algae (Microcoleus)
Belong to, anabena (Anabaena) belongs to, chroococcoid (Chrococcus) belongs to, glutinous ball algae (Gloecapsa) belongs to, Xi Zao
(Phormidium) belong to, become discrimination algae (Scytonema) category, cytoalgae (Synechocystis) belongs to, eyebrow algae (Calothrix) belongs to
And one of single discrimination algae (Tolypothrix) category.
5. barren land restoration of the ecosystem composition according to claim 1, it is characterised in that:
The barren land be desert, waste coal mine, oil pollution, volcano lacquer putty, toxic mineral or trade waste cemetery
Institute, rock and one of bald mountain.
6. a kind of barren land ecological restoring method, which is characterized in that
Barren land restoration of the ecosystem described in any one of claims 1 to 5 is introduced to be repaired with composition.
7. barren land ecological restoring method according to claim 6, it is characterised in that:
The barren land be desert, waste coal mine, oil pollution, volcano lacquer putty, toxic mineral or trade waste cemetery
Institute, rock and one of bald mountain.
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CN106269844A (en) * | 2016-11-04 | 2017-01-04 | 金福兴 | A kind of restorative procedure of mercury ion contaminated soil |
CN107999524A (en) * | 2017-12-06 | 2018-05-08 | 湖南农业大学 | A kind of method that heavy metal cadmium arsenic in rice field is passivated using biological breadcrust |
CN108396001B (en) * | 2018-02-14 | 2019-03-01 | 新疆隆博叶希丽生态环保有限公司 | Desert algae mixed liquor and the method for application and sand control with biological measures |
CN108676561B (en) * | 2018-04-23 | 2020-04-24 | 大连理工大学 | In-situ preparation method and application of coastal petroleum polluted soil remediation agent |
CN110054859A (en) * | 2019-04-19 | 2019-07-26 | 苏州国建慧投矿物新材料有限公司 | Modified alta-mud and preparation method thereof |
CN110140602B (en) * | 2019-06-14 | 2022-02-11 | 国家能源投资集团有限责任公司 | Method for recovering vegetation in coal mine area of arid area |
CN112375573A (en) * | 2020-10-27 | 2021-02-19 | 中国科学院西北生态环境资源研究院 | Substrate material for biological sand fixation, biological sand fixation material and sand fixation method |
CN115247132B (en) * | 2021-04-26 | 2024-04-16 | 中国科学院微生物研究所 | Method for controlling desert by combined artificial biological crust |
CN113857235B (en) * | 2021-08-04 | 2023-06-13 | 江西省生态环境科学研究与规划院 | Biological crust repair material for promoting ecological restoration of ionic rare earth tailing area, application and repair method |
CN114197435A (en) * | 2022-01-17 | 2022-03-18 | 新疆金正生物科技有限公司 | Microalgae sand prevention and fixation method |
CN114988964B (en) * | 2022-07-04 | 2023-09-29 | 上海市园林科学规划研究院 | Application of microalgae compound conditioner in soil improvement of urban relocation place |
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