WO1989009199A1 - Process for the production of fertiliser - Google Patents
Process for the production of fertiliser Download PDFInfo
- Publication number
- WO1989009199A1 WO1989009199A1 PCT/GB1988/000234 GB8800234W WO8909199A1 WO 1989009199 A1 WO1989009199 A1 WO 1989009199A1 GB 8800234 W GB8800234 W GB 8800234W WO 8909199 A1 WO8909199 A1 WO 8909199A1
- Authority
- WO
- WIPO (PCT)
- Prior art keywords
- seaweed
- digester
- process according
- slurry
- animal manure
- 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.)
- Ceased
Links
Classifications
-
- C—CHEMISTRY; METALLURGY
- C12—BIOCHEMISTRY; BEER; SPIRITS; WINE; VINEGAR; MICROBIOLOGY; ENZYMOLOGY; MUTATION OR GENETIC ENGINEERING
- C12P—FERMENTATION OR ENZYME-USING PROCESSES TO SYNTHESISE A DESIRED CHEMICAL COMPOUND OR COMPOSITION OR TO SEPARATE OPTICAL ISOMERS FROM A RACEMIC MIXTURE
- C12P27/00—Preparation of compounds containing a gibbane ring system, e.g. gibberellin
-
- A—HUMAN NECESSITIES
- A01—AGRICULTURE; FORESTRY; ANIMAL HUSBANDRY; HUNTING; TRAPPING; FISHING
- A01N—PRESERVATION OF BODIES OF HUMANS OR ANIMALS OR PLANTS OR PARTS THEREOF; BIOCIDES, e.g. AS DISINFECTANTS, AS PESTICIDES OR AS HERBICIDES; PEST REPELLANTS OR ATTRACTANTS; PLANT GROWTH REGULATORS
- A01N65/00—Biocides, pest repellants or attractants, or plant growth regulators containing material from algae, lichens, bryophyta, multi-cellular fungi or plants, or extracts thereof
- A01N65/03—Algae
-
- C—CHEMISTRY; METALLURGY
- C05—FERTILISERS; MANUFACTURE THEREOF
- C05F—ORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C, e.g. FERTILISERS FROM WASTE OR REFUSE
- C05F3/00—Fertilisers from human or animal excrements, e.g. manure
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02A—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
- Y02A40/00—Adaptation technologies in agriculture, forestry, livestock or agroalimentary production
- Y02A40/10—Adaptation technologies in agriculture, forestry, livestock or agroalimentary production in agriculture
- Y02A40/20—Fertilizers of biological origin, e.g. guano or fertilizers made from animal corpses
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02E—REDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
- Y02E50/00—Technologies for the production of fuel of non-fossil origin
- Y02E50/30—Fuel from waste, e.g. synthetic alcohol or diesel
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02P—CLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
- Y02P20/00—Technologies relating to chemical industry
- Y02P20/141—Feedstock
- Y02P20/145—Feedstock the feedstock being materials of biological origin
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W30/00—Technologies for solid waste management
- Y02W30/40—Bio-organic fraction processing; Production of fertilisers from the organic fraction of waste or refuse
Definitions
- the present invention relates to a process for the production of fertiliser and more especially to a method of producing a concentrated stable liquid fertiliser by the anaerobic icrobial conversion of a mixture of livestock manure and seaweed.
- seaweed and animal manures are recognised for their fertiliser value in the cultivation of plants. Both contain the principal plant nutrients nitrogen, phosphorus and potassium plus many minor elements (e.g. Magnesium, sulphur, sodium, calcium, zinc, iron, copper and manganese) .
- seaweed is known to contain a range of chemical substances which are collectively known as plant growth hormones (e.g. cytokinins, gibber- ellins and betaines) .
- a liquid fertiliser can be produced from seaweed by autoclaving seaweed meal at a temperature above 100°C and at superatmospheric press ⁇ ure in an aqueous solution containing sodium or potassium bicarbonate, see G.B. 661,989.
- a solution containing most of the nutrients can be obtained by filtration it is not believed to contain the more sensi ⁇ tive plant hormones. It is considered that such hormones would be reduced at such high processing temperatures and pressures.
- a further disadvantage of this process is that chemicals have to be used to prevent the alginate in the seaweed causing the extracted concentrate to set like a jelly.
- an anaerobic digester with a starting product as a slurry containing seaweed in a form that contains the desired plant growth hormones and animal manure, with a relatively low ratio between the respective solids contents of the seaweed and animal manure, the resulting digestion process is effective to solubilise not only the inorganic chemicals useful to plant growth but also the plant growth hormones of the seaweed.
- the ratio of solids contents of the seaweed and animal manure may range, for example, between 1/3 and 3/1 animal manure/seaweed, with the solids content of the feed mixture preferably being in the region of 10-20%.
- the process . of the invention thus involves the use of an anaerobic digester, which is a closed. thermally insulated vessel fitted with facilities for heating and mixing the contents and outlets for digested slurry and biogas (methane and carbon dioxide) which evolves during the fermentation process.
- anaerobic digester which is a closed. thermally insulated vessel fitted with facilities for heating and mixing the contents and outlets for digested slurry and biogas (methane and carbon dioxide) which evolves during the fermentation process.
- biogas methane and carbon dioxide
- the retention time is determined according to the type of feed materials used but is typically in the range 10 to 20 days.
- Digester operating temperature will be preferably in the mesophilic range, typically around 35°C.
- the optimum ratio of seaweed to manure, based on dry solids analyses, is dependent upon the particular raw materials used and the final product analysis required. The important factor is that the feed composition must be such as to promote the maintenance of healthy microbial ' populations. For example, the optimum ratio of seaweed to pig manure solds has been found to be around 1:1, with the feed dry solids analysis as high as 13%. There are usually inhibition problems with trying to digest animal slurries at high solids levels due to high ammonia levels.
- the product of the process may be applied by sprayer as a foliar feed, in which case it is necessary to remove solid particles which would cause blockages.
- Agricultural sprayers may typically have gauze filters as fine as 150 ⁇ m.
- Solids removal can be achieved by use of a suitable filtration device such as a vacuum assisted filter belt press, designed to squeeze the liquid through a woven belt with sub 150 ⁇ m apertures.
- the dewatered solids can be used as the basis for a soil conditioner byproduct.
- the water is removed without the use of high temperatures.
- This requirement can be met by the use of the principle of membrane separation in the form of reverse osmosis.
- the filtrate supplied to the reverse osmosis plant is acidified from its natural ' pH in the typical range 7.8 - 8.3 to below pH7, for example using orthophosphoric acid or acetic acid. Strongly oxidising acids should be avoided as they are likely to denature the more sensitive growth hormones in the product.
- the resultant concentrate has a typical dry solids analysis of 15%, with which soluble additives may be- blended to meet particular product requirements.
- Stabilisation of the product can be achieved in two ways. Firstly, acidification of the concentrate, preferably to below pH 6.5, inhibits further microbial acitivity and keeps ammoniacal nitrogen in solution. Secondly, the addition of formaldehyde solution at the rate of up to 2% by volume to the concentrated product acts as a biocide and odour modifier.
- the process raw materials were pig slurry with a dry solids concentration of 10%, i.e. dung and urine collected beneath slats in an intensive meal-fed pig fattening unit, and commercial Ascophyllum seaweed, in the form of meal with a dried solids content of 89%.
- Such seaweed ' meal is commercially available in the form of dried, ground seaweed and is conventionally used for the product ⁇ ion of alginate.
- the blended feed slurry comprised 50% pig solids and 50% seaweed solids with a mixture dry solids concentration of approximately 13%. This was achieved by calculating the solids present in the given volume of pig slurry and adding seaweed meal to give the equivalent dry solids.
- the anaerobic digester comprises a closed tower
- the tower At the upper end the tower is provided with an outlet 4 for biogas, and a weir 5 constructed in the form of a branched outlet pipe having an upwardly directed vent outlet 6 and a downwardly directed outlet 7 for the product of the digester.
- the lower region of the tower 1 is provided with an plurality of heat exchangers 8, typically four in number, constructed in the form of hollow tubular jackets through which heating medium can be recirculated via pipe work not shown and connected, for example. to a heating system fired by the biogas product from the digester.
- the outlet 4 of the digester is coupled on the one hand to an outlet 9 connected to a gas storage system, and on the other hand to an inlet of a recirculat ⁇ ing pump 10 by means of which the biogas can be recircul ⁇ ated through injectors 11 directed upwardly into the bases of the vertical hollow heat exchangers 8.
- a distri ⁇ butor valve 12 may serve to connect each injector 11 in turn to the outlet of the pump 10, so that jets of the biogas are forced through each of the heat exchangers 8 at regular intervals. Efficient dispersal of the solid content of the starting product into the contents of the digester can thus be achieved whilst promoting circulation thereof through the heat exchangers.
- An anaerobic digester was operated under steady state conditions in a semi-continuous mode, the heat exchangers being controlled to maintain a temperature of 37°C, and the rate of feed of starting product from the mixing tank 3 being such as to achieve hydraulic retention times of 10, 15 and 20 days, depending upon production requirements.
- the digester was fed hourly during the day, with simultaneous mixing in the manner described above to disperse the feed into the digester contents.
- Concentration of the filtered liquid was achieved by firstly acidifying with orthophosphoric acid to reduce the pH from 7.8 to 6.0, then recirculating through a reverse osmosis unit 16, operating at 40 bar pressure and a temperature of 35°C, until a product solids concen ⁇ tration of 15% was reached, as indicated diagrammatically by outlet arrow 17, waste water being discharged at 18.
- Product stabilisation and odour modification was achieved by adding 1% v/v formaldehyde solution prior to storage.
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- Life Sciences & Earth Sciences (AREA)
- Engineering & Computer Science (AREA)
- Health & Medical Sciences (AREA)
- Organic Chemistry (AREA)
- Chemical & Material Sciences (AREA)
- Biotechnology (AREA)
- General Health & Medical Sciences (AREA)
- Wood Science & Technology (AREA)
- Zoology (AREA)
- Microbiology (AREA)
- Bioinformatics & Cheminformatics (AREA)
- Plant Pathology (AREA)
- General Chemical & Material Sciences (AREA)
- General Engineering & Computer Science (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Genetics & Genomics (AREA)
- Natural Medicines & Medicinal Plants (AREA)
- Agronomy & Crop Science (AREA)
- Mycology (AREA)
- Biochemistry (AREA)
- Dentistry (AREA)
- Environmental Sciences (AREA)
- Fertilizers (AREA)
- Detergent Compositions (AREA)
- Preparation Of Compounds By Using Micro-Organisms (AREA)
- Agricultural Chemicals And Associated Chemicals (AREA)
- Processing Of Solid Wastes (AREA)
Abstract
Plant growth hormones are extracted from seaweed in an anaerobic digestion process wherein seaweed, preferably in the form of seaweed meal, is mixed with animal manure, typically pig slurry, in a solids ratio of 1:3 to 3:1 with a total solids content of 10-15 %. The digester is operated in the mesophilic temperature range, typically about 35C, with retention times of between 10 and 20 days. The digester product is filtered and concentrated to form a liquid foliar feed suitable for application to crops by spraying.
Description
PROCESS FOR THE PRODUCTION OF FERTILISER
The present invention relates to a process for the production of fertiliser and more especially to a method of producing a concentrated stable liquid fertiliser by the anaerobic icrobial conversion of a mixture of livestock manure and seaweed.
Both seaweed and animal manures are recognised for their fertiliser value in the cultivation of plants. Both contain the principal plant nutrients nitrogen, phosphorus and potassium plus many minor elements (e.g. Magnesium, sulphur, sodium, calcium, zinc, iron, copper and manganese) . In addition, seaweed is known to contain a range of chemical substances which are collectively known as plant growth hormones (e.g. cytokinins, gibber- ellins and betaines) .
It is known that a liquid fertiliser can be produced from seaweed by autoclaving seaweed meal at a temperature above 100°C and at superatmospheric press¬ ure in an aqueous solution containing sodium or potassium bicarbonate, see G.B. 661,989. Although a solution containing most of the nutrients can be obtained by filtration it is not believed to contain the more sensi¬ tive plant hormones. It is considered that such hormones would be reduced at such high processing temperatures and pressures. A further disadvantage of this process is that chemicals have to be used to prevent the alginate in the seaweed causing the extracted concentrate to set like a jelly.
It has further been proposed - see G.B. 1,559,760 to obtain a liquid product useful as a fertiliser by the anaerobic digestion of organic matter fed in slurry form to an anaerobic converter containing a culture
of micro-organisms derived from a suitable source. Although a variety of sources of organic matter are suggested, including seaweed residues and pig slurry, the liquid products of this process are indicated as being of value to plant growth only in so far as the appropriate inorganic chemicals are contained in the resulting solution.
It is an object of the present invention to provide an improved process for the extraction of plant growth nutrients from seaweed in liquid form which yields not only the inorganic chemicals but also con¬ serves the more sensitive plant growth hormones . that would be destroyed by high processing temperatures. It is a further object of the invention to provide such a process that requires a low energy input.
In accordance with the present invention, it has been found that by feeding an anaerobic digester with a starting product as a slurry containing seaweed in a form that contains the desired plant growth hormones and animal manure, with a relatively low ratio between the respective solids contents of the seaweed and animal manure, the resulting digestion process is effective to solubilise not only the inorganic chemicals useful to plant growth but also the plant growth hormones of the seaweed.
The ratio of solids contents of the seaweed and animal manure may range, for example, between 1/3 and 3/1 animal manure/seaweed, with the solids content of the feed mixture preferably being in the region of 10-20%.
The process . of the invention thus involves the use of an anaerobic digester, which is a closed.
thermally insulated vessel fitted with facilities for heating and mixing the contents and outlets for digested slurry and biogas (methane and carbon dioxide) which evolves during the fermentation process. Although the digestion can be operated under a batch regime, it is preferable to run the system semi-continuously, feeding and discharging small volumes of slurry several times a day to achieve the required volumetric retention time. The retention time is determined according to the type of feed materials used but is typically in the range 10 to 20 days. Digester operating temperature will be preferably in the mesophilic range, typically around 35°C.
Preparation of the digester feed material in¬ volves mixing seaweed, preferably in the form of seaweed meal, and livestock manure with, if necessary, additional water to form a slurry. The optimum ratio of seaweed to manure, based on dry solids analyses, is dependent upon the particular raw materials used and the final product analysis required. The important factor is that the feed composition must be such as to promote the maintenance of healthy microbial ' populations. For example, the optimum ratio of seaweed to pig manure solds has been found to be around 1:1, with the feed dry solids analysis as high as 13%. There are usually inhibition problems with trying to digest animal slurries at high solids levels due to high ammonia levels. By mixing with seaweed, which is about 45% carbohydrate, a better carbon:nitrogen ratio has been found to be achieved, which promotes good digestion. The upper limits, in digestion terms, for solids in the present mixture are more likely to be set by the physical pro¬ blems of pumping and mixing very thick slurries. Product analyses were found to be independent of retention times in the range 10 to 20 days, thereby allowing great flexibility in the rate of production from the digester installation.
- A -
The product of the process may be applied by sprayer as a foliar feed, in which case it is necessary to remove solid particles which would cause blockages. Agricultural sprayers may typically have gauze filters as fine as 150μm. Solids removal can be achieved by use of a suitable filtration device such as a vacuum assisted filter belt press, designed to squeeze the liquid through a woven belt with sub 150μm apertures. The dewatered solids can be used as the basis for a soil conditioner byproduct.
To reduce the volume of the liquid product for the purposes of economic packaging and transport and convenience of use, it is advantageous to have a concen¬ tration stage. In this the water is removed without the use of high temperatures. This requirement can be met by the use of the principle of membrane separation in the form of reverse osmosis. Preferably the filtrate supplied to the reverse osmosis plant is acidified from its natural ' pH in the typical range 7.8 - 8.3 to below pH7, for example using orthophosphoric acid or acetic acid. Strongly oxidising acids should be avoided as they are likely to denature the more sensitive growth hormones in the product. The resultant concentrate has a typical dry solids analysis of 15%, with which soluble additives may be- blended to meet particular product requirements.
Stabilisation of the product can be achieved in two ways. Firstly, acidification of the concentrate, preferably to below pH 6.5, inhibits further microbial acitivity and keeps ammoniacal nitrogen in solution. Secondly, the addition of formaldehyde solution at the rate of up to 2% by volume to the concentrated product acts as a biocide and odour modifier.
EXAMPLE
In one example of the process of the invention, the process raw materials were pig slurry with a dry solids concentration of 10%, i.e. dung and urine collected beneath slats in an intensive meal-fed pig fattening unit, and commercial Ascophyllum seaweed, in the form of meal with a dried solids content of 89%. Such seaweed 'meal is commercially available in the form of dried, ground seaweed and is conventionally used for the product¬ ion of alginate. The blended feed slurry comprised 50% pig solids and 50% seaweed solids with a mixture dry solids concentration of approximately 13%. This was achieved by calculating the solids present in the given volume of pig slurry and adding seaweed meal to give the equivalent dry solids.
The process plant utilised in this example of the invention is illustrated diagrammatically in the accompanying drawing which is a sectional elevation of an anaerobic digester, with associated equipment shown in block form.
The anaerobic digester comprises a closed tower
1 provided in the region of the lower end with an inlet
2 through which the starting materials can be pumped from a preliminary mixing tank 3. At the upper end the tower is provided with an outlet 4 for biogas, and a weir 5 constructed in the form of a branched outlet pipe having an upwardly directed vent outlet 6 and a downwardly directed outlet 7 for the product of the digester. The lower region of the tower 1 is provided with an plurality of heat exchangers 8, typically four in number, constructed in the form of hollow tubular jackets through which heating medium can be recirculated via pipe work not shown and connected, for example.
to a heating system fired by the biogas product from the digester. The outlet 4 of the digester is coupled on the one hand to an outlet 9 connected to a gas storage system, and on the other hand to an inlet of a recirculat¬ ing pump 10 by means of which the biogas can be recircul¬ ated through injectors 11 directed upwardly into the bases of the vertical hollow heat exchangers 8. A distri¬ butor valve 12 may serve to connect each injector 11 in turn to the outlet of the pump 10, so that jets of the biogas are forced through each of the heat exchangers 8 at regular intervals. Efficient dispersal of the solid content of the starting product into the contents of the digester can thus be achieved whilst promoting circulation thereof through the heat exchangers.
An anaerobic digester was operated under steady state conditions in a semi-continuous mode, the heat exchangers being controlled to maintain a temperature of 37°C, and the rate of feed of starting product from the mixing tank 3 being such as to achieve hydraulic retention times of 10, 15 and 20 days, depending upon production requirements. The digester was fed hourly during the day, with simultaneous mixing in the manner described above to disperse the feed into the digester contents.
An important benefit of digestion was found to be that the alginate (constituting part of the carbo¬ hydrate above) from the seaweed is broken down so that the extract concentrate does not set like a jelly. The fact that alginate is denatured during digestion and that a large proportion of the biogas generated in the digestion process is apparently due to the presence of the seaweed is a surprising result which is contrary to the indications of prior research that the long chain molecules in alginate were resistant to attack by anaerobic bacteria.
Digested slurry with a dry solids content of 8.5% was displaced over the digester overflow weir 5 to a vacuum assisted belt press 13, fitted with a woven textile belt with approximately 125μm apertures. The resultant filtered liquid of 4.7% dry solids content was stored in a holding tank 14. Dewatered fibre of 24% dry solids content was also produced as indicated by outlet arrow 15.
Concentration of the filtered liquid was achieved by firstly acidifying with orthophosphoric acid to reduce the pH from 7.8 to 6.0, then recirculating through a reverse osmosis unit 16, operating at 40 bar pressure and a temperature of 35°C, until a product solids concen¬ tration of 15% was reached, as indicated diagrammatically by outlet arrow 17, waste water being discharged at 18.
Product stabilisation and odour modification was achieved by adding 1% v/v formaldehyde solution prior to storage.
Claims
1. A process for extracting plant growth hormones from seaweed, characterised in that the seaweed is fed to an anaerobic digester in the form of a slurry in admixture with animal manure whereby such hormones are obtained in the liquid phase of the product of the digester.
2. A process according to Claim 1 wherein said slurry of seaweed and animal manure is prepared utilising seaweed in the form of seaweed meal.
3. A process according to Claim 1 or 2 wherein said animal manure is pig slurry.
4. A process according to any one of Claims 1-3, wherein the slurry of seaweed and animal manure comprises a ratio of seaweed/animal manure of from 1:3 to 3:1 solids content, by weight.
5. A process according to Claim 4, wherein said ratio is approximately 1:1.
6. A process according to any one of Claims 1-5, wherein the said digester is operated to provide a hydraulic retention time of the contents of from 10 to 20 days, and the content of the digester is maintained at a temperature in the mesophilic range.
7. A process according to Claim 6, wherein said temperature is approximately 35°C.
8. A process according to any one of Claims 1-7, wherein the initial solids content of said slurry of seaweed/animal manure is from 10-15%, by weight.
9. A process according to any one of Claims 1-8, wherein the solids content of the slurry within the anaerobic digester is mantained in suspension therein by forced recirculation of the biogas product of the digester through injector nozzles located in the lower region of the digester.
10. A liquid organic foliar feed produced by filtrat¬ ion and concentration of the product of the digestion process according to any one of Claims 1-9.
Priority Applications (9)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP63502760A JPH03504845A (en) | 1988-03-28 | 1988-03-28 | Fertilizer manufacturing method |
| EP88902882A EP0408547B1 (en) | 1988-03-28 | 1988-03-28 | Process for the production of fertiliser |
| AT88902882T ATE86238T1 (en) | 1988-03-28 | 1988-03-28 | PROCESS FOR MANUFACTURE OF FERTILIZER. |
| DE8888902882T DE3878928T2 (en) | 1988-03-28 | 1988-03-28 | METHOD FOR PRODUCING FERTILIZERS. |
| AU14984/88A AU620030B2 (en) | 1988-03-28 | 1988-03-28 | Process for the production of fertiliser |
| PCT/GB1988/000234 WO1989009199A1 (en) | 1988-03-28 | 1988-03-28 | Process for the production of fertiliser |
| DK221590A DK221590A (en) | 1988-03-28 | 1990-09-14 | PROCEDURE FOR MANUFACTURE OF FERTILIZERS |
| NO90904214A NO904214L (en) | 1988-03-28 | 1990-09-27 | PROCEDURE FOR MANUFACTURING FERTILIZERS. |
| GB9021355A GB2236313B (en) | 1988-03-28 | 1990-09-28 | Process for the production of fertiliser |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| PCT/GB1988/000234 WO1989009199A1 (en) | 1988-03-28 | 1988-03-28 | Process for the production of fertiliser |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| WO1989009199A1 true WO1989009199A1 (en) | 1989-10-05 |
Family
ID=10629579
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| PCT/GB1988/000234 Ceased WO1989009199A1 (en) | 1988-03-28 | 1988-03-28 | Process for the production of fertiliser |
Country Status (9)
| Country | Link |
|---|---|
| EP (1) | EP0408547B1 (en) |
| JP (1) | JPH03504845A (en) |
| AT (1) | ATE86238T1 (en) |
| AU (1) | AU620030B2 (en) |
| DE (1) | DE3878928T2 (en) |
| DK (1) | DK221590A (en) |
| GB (1) | GB2236313B (en) |
| NO (1) | NO904214L (en) |
| WO (1) | WO1989009199A1 (en) |
Cited By (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| FR2717796A1 (en) * | 1994-03-22 | 1995-09-29 | Le Berre Erwan | Odorous liquid fertilizer and process for manufacturing such a fertilizer. |
| CN109650971A (en) * | 2018-12-24 | 2019-04-19 | 贵州省烟草公司遵义市公司 | A kind of foliar fertilizer and preparation method thereof promoting the secretion of tobacco oil |
Families Citing this family (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| GB2313116A (en) * | 1996-05-13 | 1997-11-19 | Biomass Recycling Ltd | Treatment of wastes |
Citations (8)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| FR1146820A (en) * | 1956-02-16 | 1957-11-15 | Process for destroying urban and household waste | |
| AU480689B2 (en) * | 1971-11-11 | 1974-05-09 | Samamatic Tanks Proprietary Limited | Method for anaerobic fermentation |
| DE2354270A1 (en) * | 1973-10-30 | 1975-05-07 | Alfred Hoehn | Fast composting and prepn of (floating) water vegetation - involves a slurry of the vegetation with inocculation sludge |
| FR2265288A1 (en) * | 1974-04-02 | 1975-10-24 | Liquichimica Spa | Decolouration of physiological algaes with carbon source - in culture medium under action of light and opt cellulosic bacteria |
| FR2398110A1 (en) * | 1977-07-21 | 1979-02-16 | Grenet Edouard | Treating organic waste by anaerobic fermentation - to produce methane and dry residue for animal feed |
| FR2516542A1 (en) * | 1981-11-18 | 1983-05-20 | Inst Francais Du Petrole | Fuel gas prodn. by anaerobic fermentation of algae - and co-substrate with high insolubles content |
| EP0152685A1 (en) * | 1983-11-30 | 1985-08-28 | Clearfield N.V. | Fertilizer |
| EP0167984A1 (en) * | 1984-07-09 | 1986-01-15 | COMPAGNIE GENERALE D'ELECTRICITE Société anonyme dite: | Process for the obtention of methane by fermentation of algae |
Family Cites Families (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| GB2150551A (en) * | 1983-11-30 | 1985-07-03 | Clearfield Nv | Fertiliser from seaweed |
-
1988
- 1988-03-28 WO PCT/GB1988/000234 patent/WO1989009199A1/en not_active Ceased
- 1988-03-28 EP EP88902882A patent/EP0408547B1/en not_active Expired - Lifetime
- 1988-03-28 DE DE8888902882T patent/DE3878928T2/en not_active Expired - Fee Related
- 1988-03-28 AU AU14984/88A patent/AU620030B2/en not_active Ceased
- 1988-03-28 JP JP63502760A patent/JPH03504845A/en active Pending
- 1988-03-28 AT AT88902882T patent/ATE86238T1/en not_active IP Right Cessation
-
1990
- 1990-09-14 DK DK221590A patent/DK221590A/en not_active Application Discontinuation
- 1990-09-27 NO NO90904214A patent/NO904214L/en unknown
- 1990-09-28 GB GB9021355A patent/GB2236313B/en not_active Expired - Lifetime
Patent Citations (8)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| FR1146820A (en) * | 1956-02-16 | 1957-11-15 | Process for destroying urban and household waste | |
| AU480689B2 (en) * | 1971-11-11 | 1974-05-09 | Samamatic Tanks Proprietary Limited | Method for anaerobic fermentation |
| DE2354270A1 (en) * | 1973-10-30 | 1975-05-07 | Alfred Hoehn | Fast composting and prepn of (floating) water vegetation - involves a slurry of the vegetation with inocculation sludge |
| FR2265288A1 (en) * | 1974-04-02 | 1975-10-24 | Liquichimica Spa | Decolouration of physiological algaes with carbon source - in culture medium under action of light and opt cellulosic bacteria |
| FR2398110A1 (en) * | 1977-07-21 | 1979-02-16 | Grenet Edouard | Treating organic waste by anaerobic fermentation - to produce methane and dry residue for animal feed |
| FR2516542A1 (en) * | 1981-11-18 | 1983-05-20 | Inst Francais Du Petrole | Fuel gas prodn. by anaerobic fermentation of algae - and co-substrate with high insolubles content |
| EP0152685A1 (en) * | 1983-11-30 | 1985-08-28 | Clearfield N.V. | Fertilizer |
| EP0167984A1 (en) * | 1984-07-09 | 1986-01-15 | COMPAGNIE GENERALE D'ELECTRICITE Société anonyme dite: | Process for the obtention of methane by fermentation of algae |
Non-Patent Citations (2)
| Title |
|---|
| Equinoxe, no. 3, June/July 1985, (Nantes, FR), P. Mancliere: "Methanisation des algues De l'Energie a revendre ?", pages 7-12 * |
| Progress in Energy and Combustion Science, volume 8, no. 2, 1982, Pergamon Press Ltd, (Oxford, GB), P.N. Hobson et al.: "Production and use of biogas in agriculture", pages 135-158 * |
Cited By (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| FR2717796A1 (en) * | 1994-03-22 | 1995-09-29 | Le Berre Erwan | Odorous liquid fertilizer and process for manufacturing such a fertilizer. |
| CN109650971A (en) * | 2018-12-24 | 2019-04-19 | 贵州省烟草公司遵义市公司 | A kind of foliar fertilizer and preparation method thereof promoting the secretion of tobacco oil |
Also Published As
| Publication number | Publication date |
|---|---|
| GB2236313B (en) | 1992-02-12 |
| DK221590D0 (en) | 1990-09-14 |
| GB9021355D0 (en) | 1990-11-28 |
| JPH03504845A (en) | 1991-10-24 |
| EP0408547B1 (en) | 1993-03-03 |
| DE3878928T2 (en) | 1993-06-17 |
| AU1498488A (en) | 1989-10-16 |
| NO904214D0 (en) | 1990-09-27 |
| EP0408547A1 (en) | 1991-01-23 |
| AU620030B2 (en) | 1992-02-13 |
| DK221590A (en) | 1990-09-14 |
| GB2236313A (en) | 1991-04-03 |
| DE3878928D1 (en) | 1993-04-08 |
| ATE86238T1 (en) | 1993-03-15 |
| NO904214L (en) | 1990-09-27 |
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