JPH04507217A - Methods and apparatus for treating materials from which methane and other chemicals harmful to the environment are released - Google Patents
Methods and apparatus for treating materials from which methane and other chemicals harmful to the environment are releasedInfo
- Publication number
- JPH04507217A JPH04507217A JP2511502A JP51150290A JPH04507217A JP H04507217 A JPH04507217 A JP H04507217A JP 2511502 A JP2511502 A JP 2511502A JP 51150290 A JP51150290 A JP 51150290A JP H04507217 A JPH04507217 A JP H04507217A
- Authority
- JP
- Japan
- Prior art keywords
- gas
- combustion
- cleaning
- methane
- starting material
- 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.)
- Pending
Links
- VNWKTOKETHGBQD-UHFFFAOYSA-N methane Chemical compound C VNWKTOKETHGBQD-UHFFFAOYSA-N 0.000 title claims description 31
- 238000000034 method Methods 0.000 title claims description 23
- 239000000463 material Substances 0.000 title claims description 8
- 239000000126 substance Substances 0.000 title claims description 8
- 239000007789 gas Substances 0.000 claims description 45
- 239000003337 fertilizer Substances 0.000 claims description 31
- MWUXSHHQAYIFBG-UHFFFAOYSA-N nitrogen oxide Inorganic materials O=[N] MWUXSHHQAYIFBG-UHFFFAOYSA-N 0.000 claims description 27
- 238000004140 cleaning Methods 0.000 claims description 25
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 23
- QGZKDVFQNNGYKY-UHFFFAOYSA-N Ammonia Chemical compound N QGZKDVFQNNGYKY-UHFFFAOYSA-N 0.000 claims description 22
- 238000002485 combustion reaction Methods 0.000 claims description 20
- 239000000292 calcium oxide Substances 0.000 claims description 16
- ODINCKMPIJJUCX-UHFFFAOYSA-N calcium oxide Inorganic materials [Ca]=O ODINCKMPIJJUCX-UHFFFAOYSA-N 0.000 claims description 16
- 239000000567 combustion gas Substances 0.000 claims description 15
- 229910021529 ammonia Inorganic materials 0.000 claims description 11
- BRPQOXSCLDDYGP-UHFFFAOYSA-N calcium oxide Chemical compound [O-2].[Ca+2] BRPQOXSCLDDYGP-UHFFFAOYSA-N 0.000 claims description 11
- 238000010438 heat treatment Methods 0.000 claims description 11
- 239000010802 sludge Substances 0.000 claims description 11
- VHUUQVKOLVNVRT-UHFFFAOYSA-N Ammonium hydroxide Chemical compound [NH4+].[OH-] VHUUQVKOLVNVRT-UHFFFAOYSA-N 0.000 claims description 10
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 claims description 10
- RWSOTUBLDIXVET-UHFFFAOYSA-N Dihydrogen sulfide Chemical compound S RWSOTUBLDIXVET-UHFFFAOYSA-N 0.000 claims description 10
- 235000011114 ammonium hydroxide Nutrition 0.000 claims description 10
- ZCCIPPOKBCJFDN-UHFFFAOYSA-N calcium nitrate Chemical compound [Ca+2].[O-][N+]([O-])=O.[O-][N+]([O-])=O ZCCIPPOKBCJFDN-UHFFFAOYSA-N 0.000 claims description 10
- 229910000037 hydrogen sulfide Inorganic materials 0.000 claims description 10
- NLXLAEXVIDQMFP-UHFFFAOYSA-N Ammonium chloride Substances [NH4+].[Cl-] NLXLAEXVIDQMFP-UHFFFAOYSA-N 0.000 claims description 9
- NINIDFKCEFEMDL-UHFFFAOYSA-N Sulfur Chemical compound [S] NINIDFKCEFEMDL-UHFFFAOYSA-N 0.000 claims description 9
- 239000011593 sulfur Substances 0.000 claims description 9
- 229910019142 PO4 Inorganic materials 0.000 claims description 8
- 239000007858 starting material Substances 0.000 claims description 8
- 238000003860 storage Methods 0.000 claims description 8
- 210000003608 fece Anatomy 0.000 claims description 7
- 229910052717 sulfur Inorganic materials 0.000 claims description 7
- 239000010452 phosphate Substances 0.000 claims description 6
- NBIIXXVUZAFLBC-UHFFFAOYSA-K phosphate Chemical compound [O-]P([O-])([O-])=O NBIIXXVUZAFLBC-UHFFFAOYSA-K 0.000 claims description 6
- 229910052815 sulfur oxide Inorganic materials 0.000 claims description 6
- 229910052757 nitrogen Inorganic materials 0.000 claims description 5
- OYPRJOBELJOOCE-UHFFFAOYSA-N Calcium Chemical compound [Ca] OYPRJOBELJOOCE-UHFFFAOYSA-N 0.000 claims description 4
- 239000011575 calcium Substances 0.000 claims description 4
- 229910052791 calcium Inorganic materials 0.000 claims description 4
- OSGAYBCDTDRGGQ-UHFFFAOYSA-L calcium sulfate Chemical compound [Ca+2].[O-]S([O-])(=O)=O OSGAYBCDTDRGGQ-UHFFFAOYSA-L 0.000 claims description 4
- 239000007788 liquid Substances 0.000 claims description 4
- 239000010871 livestock manure Substances 0.000 claims description 4
- XTQHKBHJIVJGKJ-UHFFFAOYSA-N sulfur monoxide Chemical class S=O XTQHKBHJIVJGKJ-UHFFFAOYSA-N 0.000 claims description 3
- 238000005406 washing Methods 0.000 claims description 3
- 238000006243 chemical reaction Methods 0.000 claims description 2
- 238000002156 mixing Methods 0.000 claims description 2
- 238000000746 purification Methods 0.000 claims description 2
- 230000000087 stabilizing effect Effects 0.000 claims description 2
- 239000002351 wastewater Substances 0.000 claims description 2
- UQSXHKLRYXJYBZ-UHFFFAOYSA-N Iron oxide Chemical compound [Fe]=O UQSXHKLRYXJYBZ-UHFFFAOYSA-N 0.000 claims 2
- 244000144972 livestock Species 0.000 claims 1
- 238000003672 processing method Methods 0.000 claims 1
- 239000000243 solution Substances 0.000 description 9
- XEEYBQQBJWHFJM-UHFFFAOYSA-N Iron Chemical compound [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 description 6
- 235000021317 phosphate Nutrition 0.000 description 6
- 239000000203 mixture Substances 0.000 description 5
- 235000014413 iron hydroxide Nutrition 0.000 description 4
- NCNCGGDMXMBVIA-UHFFFAOYSA-L iron(ii) hydroxide Chemical compound [OH-].[OH-].[Fe+2] NCNCGGDMXMBVIA-UHFFFAOYSA-L 0.000 description 4
- 239000002245 particle Substances 0.000 description 4
- 239000002253 acid Substances 0.000 description 3
- 239000000428 dust Substances 0.000 description 3
- 229910052500 inorganic mineral Inorganic materials 0.000 description 3
- 229910052742 iron Inorganic materials 0.000 description 3
- 239000011707 mineral Substances 0.000 description 3
- 150000003839 salts Chemical class 0.000 description 3
- 101150054854 POU1F1 gene Proteins 0.000 description 2
- NBIIXXVUZAFLBC-UHFFFAOYSA-N Phosphoric acid Chemical group OP(O)(O)=O NBIIXXVUZAFLBC-UHFFFAOYSA-N 0.000 description 2
- OAICVXFJPJFONN-UHFFFAOYSA-N Phosphorus Chemical compound [P] OAICVXFJPJFONN-UHFFFAOYSA-N 0.000 description 2
- QAOWNCQODCNURD-UHFFFAOYSA-N Sulfuric acid Chemical compound OS(O)(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-N 0.000 description 2
- 238000003916 acid precipitation Methods 0.000 description 2
- 239000002956 ash Substances 0.000 description 2
- 239000001506 calcium phosphate Substances 0.000 description 2
- 229910000389 calcium phosphate Inorganic materials 0.000 description 2
- 235000011010 calcium phosphates Nutrition 0.000 description 2
- 238000009833 condensation Methods 0.000 description 2
- 230000005494 condensation Effects 0.000 description 2
- 239000003673 groundwater Substances 0.000 description 2
- 238000012856 packing Methods 0.000 description 2
- 150000003013 phosphoric acid derivatives Chemical class 0.000 description 2
- 239000011574 phosphorus Substances 0.000 description 2
- 229910052698 phosphorus Inorganic materials 0.000 description 2
- 238000012545 processing Methods 0.000 description 2
- 150000004760 silicates Chemical class 0.000 description 2
- 239000008399 tap water Substances 0.000 description 2
- 235000020679 tap water Nutrition 0.000 description 2
- 230000032258 transport Effects 0.000 description 2
- QORWJWZARLRLPR-UHFFFAOYSA-H tricalcium bis(phosphate) Chemical compound [Ca+2].[Ca+2].[Ca+2].[O-]P([O-])([O-])=O.[O-]P([O-])([O-])=O QORWJWZARLRLPR-UHFFFAOYSA-H 0.000 description 2
- 241000283690 Bos taurus Species 0.000 description 1
- 229910021532 Calcite Inorganic materials 0.000 description 1
- MBMLMWLHJBBADN-UHFFFAOYSA-N Ferrous sulfide Chemical compound [Fe]=S MBMLMWLHJBBADN-UHFFFAOYSA-N 0.000 description 1
- 235000002918 Fraxinus excelsior Nutrition 0.000 description 1
- VEXZGXHMUGYJMC-UHFFFAOYSA-N Hydrochloric acid Chemical compound Cl VEXZGXHMUGYJMC-UHFFFAOYSA-N 0.000 description 1
- 235000019738 Limestone Nutrition 0.000 description 1
- 229910002651 NO3 Inorganic materials 0.000 description 1
- NHNBFGGVMKEFGY-UHFFFAOYSA-N Nitrate Chemical compound [O-][N+]([O-])=O NHNBFGGVMKEFGY-UHFFFAOYSA-N 0.000 description 1
- GRYLNZFGIOXLOG-UHFFFAOYSA-N Nitric acid Chemical compound O[N+]([O-])=O GRYLNZFGIOXLOG-UHFFFAOYSA-N 0.000 description 1
- IOVCWXUNBOPUCH-UHFFFAOYSA-M Nitrite anion Chemical compound [O-]N=O IOVCWXUNBOPUCH-UHFFFAOYSA-M 0.000 description 1
- CBENFWSGALASAD-UHFFFAOYSA-N Ozone Chemical compound [O-][O+]=O CBENFWSGALASAD-UHFFFAOYSA-N 0.000 description 1
- 241000282887 Suidae Species 0.000 description 1
- LSNNMFCWUKXFEE-UHFFFAOYSA-N Sulfurous acid Chemical compound OS(O)=O LSNNMFCWUKXFEE-UHFFFAOYSA-N 0.000 description 1
- UCKMPCXJQFINFW-UHFFFAOYSA-N Sulphide Chemical compound [S-2] UCKMPCXJQFINFW-UHFFFAOYSA-N 0.000 description 1
- 229910000147 aluminium phosphate Inorganic materials 0.000 description 1
- 239000000908 ammonium hydroxide Substances 0.000 description 1
- 239000007864 aqueous solution Substances 0.000 description 1
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 1
- 238000001354 calcination Methods 0.000 description 1
- AXCZMVOFGPJBDE-UHFFFAOYSA-L calcium dihydroxide Chemical compound [OH-].[OH-].[Ca+2] AXCZMVOFGPJBDE-UHFFFAOYSA-L 0.000 description 1
- 239000000920 calcium hydroxide Substances 0.000 description 1
- 229910001861 calcium hydroxide Inorganic materials 0.000 description 1
- 244000309466 calf Species 0.000 description 1
- UHZZMRAGKVHANO-UHFFFAOYSA-M chlormequat chloride Chemical compound [Cl-].C[N+](C)(C)CCCl UHZZMRAGKVHANO-UHFFFAOYSA-M 0.000 description 1
- 235000013365 dairy product Nutrition 0.000 description 1
- 230000007423 decrease Effects 0.000 description 1
- 230000003247 decreasing effect Effects 0.000 description 1
- 238000011161 development Methods 0.000 description 1
- 235000013601 eggs Nutrition 0.000 description 1
- 238000003912 environmental pollution Methods 0.000 description 1
- 231100001261 hazardous Toxicity 0.000 description 1
- 229910052739 hydrogen Inorganic materials 0.000 description 1
- IXCSERBJSXMMFS-UHFFFAOYSA-N hydrogen chloride Substances Cl.Cl IXCSERBJSXMMFS-UHFFFAOYSA-N 0.000 description 1
- 229910000041 hydrogen chloride Inorganic materials 0.000 description 1
- 239000004615 ingredient Substances 0.000 description 1
- 239000006028 limestone Substances 0.000 description 1
- 238000004519 manufacturing process Methods 0.000 description 1
- 229910052751 metal Inorganic materials 0.000 description 1
- 239000002184 metal Substances 0.000 description 1
- 150000002739 metals Chemical class 0.000 description 1
- 238000012986 modification Methods 0.000 description 1
- 230000004048 modification Effects 0.000 description 1
- 229910017604 nitric acid Inorganic materials 0.000 description 1
- 239000001301 oxygen Substances 0.000 description 1
- 229910052760 oxygen Inorganic materials 0.000 description 1
- 230000001681 protective effect Effects 0.000 description 1
- 230000001105 regulatory effect Effects 0.000 description 1
- 230000035943 smell Effects 0.000 description 1
- 239000007787 solid Substances 0.000 description 1
- 210000002784 stomach Anatomy 0.000 description 1
- 231100000331 toxic Toxicity 0.000 description 1
- 230000002588 toxic effect Effects 0.000 description 1
- MEYZYGMYMLNUHJ-UHFFFAOYSA-N tunicamycin Natural products CC(C)CCCCCCCCCC=CC(=O)NC1C(O)C(O)C(CC(O)C2OC(C(O)C2O)N3C=CC(=O)NC3=O)OC1OC4OC(CO)C(O)C(O)C4NC(=O)C MEYZYGMYMLNUHJ-UHFFFAOYSA-N 0.000 description 1
Classifications
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- 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
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/34—Chemical or biological purification of waste gases
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F11/00—Treatment of sludge; Devices therefor
-
- C—CHEMISTRY; METALLURGY
- C05—FERTILISERS; MANUFACTURE THEREOF
- C05B—PHOSPHATIC FERTILISERS
- C05B17/00—Other phosphatic fertilisers, e.g. soft rock phosphates, bone meal
-
- 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
- Y02C—CAPTURE, STORAGE, SEQUESTRATION OR DISPOSAL OF GREENHOUSE GASES [GHG]
- Y02C20/00—Capture or disposal of greenhouse gases
- Y02C20/20—Capture or disposal of greenhouse gases of methane
-
- 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
Landscapes
- Chemical & Material Sciences (AREA)
- Engineering & Computer Science (AREA)
- Organic Chemistry (AREA)
- Environmental & Geological Engineering (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Analytical Chemistry (AREA)
- General Chemical & Material Sciences (AREA)
- Oil, Petroleum & Natural Gas (AREA)
- Health & Medical Sciences (AREA)
- Biomedical Technology (AREA)
- Life Sciences & Earth Sciences (AREA)
- Hydrology & Water Resources (AREA)
- Water Supply & Treatment (AREA)
- Fertilizers (AREA)
- Treatment Of Sludge (AREA)
- Treating Waste Gases (AREA)
- Incineration Of Waste (AREA)
Abstract
(57)【要約】本公報は電子出願前の出願データであるため要約のデータは記録されません。 (57) [Summary] This bulletin contains application data before electronic filing, so abstract data is not recorded.
Description
【発明の詳細な説明】 メタン及び環境に有害な他の m 放出される を 理 る 2 び 室 環境汚染によって惹き起こされる問題に関連して、環境に有害な化学物質を廃棄 物から除去することは極めて重要なことである。[Detailed description of the invention] Methane and other substances harmful to the environment 2 chambers that control the release Disposal of environmentally harmful chemicals related to problems caused by environmental pollution It is extremely important to remove it from objects.
乳牛、子牛、豚の肥料を輸送や保存したり地上に撒いた場合、及び排水汚泥のよ うな汚泥の輸送、保存、及び処理中に、かなりの量のメタン、アンモニア及び硫 化水素が放出される。特にアンモニア及び硫化水素は環境に非常に有害である。When manure from dairy cows, calves, and pigs is transported, stored, or spread on the ground, and when wastewater sludge is Significant amounts of methane, ammonia and sulfur are produced during transport, storage and processing of sludge. Hydrogen chloride is released. Ammonia and hydrogen sulfide in particular are very harmful to the environment.
アンモニアは化学的及び生物学的に酸化されて亜硝酸及び硝酸になり、それらは 酸性雨を生ずる。Ammonia is chemically and biologically oxidized to nitrite and nitric acid, which are Causes acid rain.
硫化水素は腐った卵のような悪臭のするガスであり、高濃度では非常に毒性の高 いものになる。この物質は酸化されて亜硫酸及び硫酸になり、それらも酸性雨の 成分になる。Hydrogen sulfide is a gas that smells like rotten eggs and is highly toxic at high concentrations. Become something. This substance is oxidized to sulfurous acid and sulfuric acid, which are also produced by acid rain. Becomes an ingredient.
メタンもオゾン層に害を与えるであろう。Methane will also harm the ozone layer.
従って、農場で大気中に流れ出るこれらの環境に有害めて重要なことである。Therefore, these environmentally hazardous emissions that are released into the atmosphere on farms are of great importance.
広義には、本発明は、メタン及び環境に有害な他の化学物質が放出される夫々の 材料を処理する方法に関し、この場合、この材料を加熱し、放出されるガスを水 又は化学的ガス洗浄循環溶液で洗浄処理にかけ、洗浄装置から放出されるガス中 のメタンを燃焼し、発生する熱を少なくとも部分的に出発材料を加熱するのに用 いる。Broadly speaking, the present invention applies to each Regarding the method of processing the material, in this case the material is heated and the gas released is immersed in water. or subjected to a cleaning process with a chemical gas cleaning circulation solution and in the gases released from the cleaning equipment. of methane and the heat generated is used at least partially to heat the starting material. There is.
燃焼中に発生した過剰の熱を、異なった加熱目的、例えば集中暖房に用いてもよ い。The excess heat generated during combustion may be used for different heating purposes, for example for central heating. stomach.
本発明の方法は、肥料及び(又は)排泄物を処理するのに用いても成功を収める ことができる。農場でこの方法を用いる場合、もし望むならば、家畜が住んでい る厩舎からの舎内空気を収り出すのと同時に、その舎内空気を向流状に同じ洗浄 装置又は別の洗浄装置で洗浄することを行なってもよい。出来るだけ良好な精製 を行わせるため、出来るだけ冷たい水、例えば12℃より低い水を洗浄に用いる のが好ましい。このような条件により、出来るだけ多くのアンモニア及び硫化水 素を向流状に洗浄されたガスから除去することができる。なぜなら、水の温度が 低いことにより、ガス流中の水蒸気の大部分が凝縮る。洗浄水として地下水中に 入れたタンクからの水を、その水は通常温度が低い(10℃)ので、用いること ができる。勿論、タンクも水道水で冷却することができる。The method of the invention can also be successfully used to treat manure and/or excreta. be able to. When using this method on the farm, if desired, At the same time as the indoor air from the stable is removed, the indoor air is also washed in a countercurrent manner. Cleaning may be carried out in the device or in a separate cleaning device. Purification as good as possible Use as cold water as possible, for example, water below 12°C, for washing. is preferable. Under these conditions, as much ammonia and sulfide water as possible can be removed. Elements can be removed from the scrubbed gas countercurrently. Because the water temperature The low temperature causes most of the water vapor in the gas stream to condense. into groundwater as cleaning water Use water from the tank you put it in, as that water is usually at a low temperature (10°C). Can be done. Of course, the tank can also be cooled with tap water.
洗浄装置では、上方へ流れるガスと、下方へ流れる水との接触を出来るだけ向上 させるため、サドル型装置のような慣用的充填床装置を適用するのが好ましい。In the cleaning equipment, the contact between the gas flowing upward and the water flowing downward is improved as much as possible. For this purpose, it is preferred to apply conventional packed bed equipment, such as saddle type equipment.
更に、上方へ粒径が減少して行く充填装置が配備された凝縮塔を通ってガスを上 方へ、その上に噴霧される水とは自流状に誘導するのが好ましい。Furthermore, the gas is passed through a condensation column equipped with a packing device whose particle size decreases upward. It is preferable that the water sprayed thereon be guided in a self-current manner.
凝縮塔の底に集められたアンモニア溶液も硫化水素を含み、それはガス流から洗 浄除去され、その硫化水素は水酸化鉄スラッジにその溶液を通すことにより硫化 鉄に転化させてもよい。形成された硫化鉄は、それから鉄を回収するため溶鉱炉 関係へ販売することができる。もし望むならば、アンモニアを水酸化アンモニウ ム溶液としてスラッジ層の上の水中に収集してもよい。凝縮装置中その溶液を循 環洗浄液体として用いる場合、その溶液のアンモニア含有量は50%にさえ上昇 してもよい。その後でタンク中の溶液を奇麗な水によって置き換えてもよい。The ammonia solution collected at the bottom of the condensation column also contains hydrogen sulfide, which is washed from the gas stream. The hydrogen sulfide is sulfurized by passing the solution through iron hydroxide sludge. May be converted to iron. The formed iron sulfide is then sent to a blast furnace to recover the iron. Can be sold to relationships. If desired, replace the ammonia with ammonium hydroxide. It may be collected in water above the sludge layer as a sludge solution. Circulating the solution through the condenser When used as a ring cleaning liquid, the ammonia content of the solution increases to even 50% You may. The solution in the tank may then be replaced with clean water.
勿論本発明による方法は、サイロに貯蔵された肥料にも適用することができる。Of course, the method according to the invention can also be applied to fertilizers stored in silos.
農場でこのように処理された肥料は殆どアンモニア及び硫化水素を含まないので 、後で通常のやり方で地面に撒いても、そうすることによって環境に有害な多量 の化学物質が大気中に流れることはない。Fertilizers treated in this way on farms contain almost no ammonia and hydrogen sulfide. , even if later spread on the ground in the usual way, doing so will result in large amounts that are harmful to the environment. of chemicals are not released into the atmosphere.
多量の余分な肥料が存在する場合、本発明の方法により加熱され濃縮されたその 余分な肥料は燃焼炉で燃焼することができる。その場合、NH,及びH,Sが除 去されたメタンガスも同じ炉で燃焼することができる。その場合、環境に有害な 硫黄酸化物及び窒素酸化物が形成される。そのことが、燃焼炉からきたそれらガ スを熱交換器を経て酸化カルシウム床に通過させる理由である。燃焼ガス中の硫 黄酸化物及び窒素酸化物と反応するCaOは、硫酸カルシウム及び硝酸カルシウ ムに転化する。更に、燐酸塩を含む鉱物残渣は燃焼空間の底に収集される。この 残渣は、硫黄及び窒素の酸化物をCaOに結合させることにより形成された燐酸 カルシウム及び硝酸カルシウムと混合することにより、カルシウム、窒素及び燐 酸塩を含む価値のある肥料を与える。If a large amount of excess fertilizer is present, it can be heated and concentrated according to the method of the invention. Excess fertilizer can be burned in a combustion furnace. In that case, NH, H, and S are excluded. The removed methane gas can also be combusted in the same furnace. In that case, environmentally harmful Sulfur oxides and nitrogen oxides are formed. This means that those gases coming from the combustion furnace This is why the gas is passed through a heat exchanger and into a bed of calcium oxide. Sulfur in combustion gas CaO, which reacts with yellow oxides and nitrogen oxides, is calcium sulfate and calcium nitrate. It transforms into a system. Additionally, mineral residues containing phosphates are collected at the bottom of the combustion space. this The residue is phosphoric acid formed by combining oxides of sulfur and nitrogen with CaO. Calcium, nitrogen and phosphorus by mixing with calcium and calcium nitrate Feed with valuable fertilizers containing acid salts.
本発明は、例えば、農場に販売され、メタンを含む洗浄されたガスの排出部が頂 部にある向流式洗浄装置を有するプラントにも関し、その排出部はメタンを燃焼 するための燃焼装置に接続され、その燃焼装置は、出発材料の貯蔵空間中に存在 する加熱管に接続された燃焼ガス用排出部を有する。The present invention can be used, for example, to sell a farm to a farm where the exhaust of the cleaned gas containing methane is This also relates to plants with counter-current cleaning equipment located in the connected to a combustion device for It has a combustion gas outlet connected to a heating tube.
そのプラントは、肥料スラッジを収集及び運搬する船の上に配置することもでき る。The plant can also be located on a ship that collects and transports fertilizer sludge. Ru.
本発明による装置の特別な態様として、厩舎の空間も洗浄装置の底にあるガス供 給部に接続され、そのため普通であれば大気中に放出されるであろう排出舎内空 気中に存在していたアンモニア及び硫化水素がそこがら回収される。As a special embodiment of the device according to the invention, the stable space is also provided with a gas supply at the bottom of the cleaning device. The air inside the exhaust building is connected to the air supply and therefore would normally be released into the atmosphere. Ammonia and hydrogen sulfide present in the air are recovered therefrom.
もし望むならば、本発明による方法及び装置により農場で生じたアンモニア溶液 を、それから濃厚な純水アンモニア溶液が製造される中心地に輸送し、然る後、 その溶液を濃厚アンモニア溶液を必要とする場所へ輸送してもよい。If desired, the ammonia solution produced on the farm by the method and apparatus according to the invention is then transported to a center where a concentrated pure ammonia solution is produced; The solution may be transported to locations where concentrated ammonia solution is required.
本発明は、上で述べたようなプラントにも関し、そのプラントは、本発明の方法 に従い処理された肥料及び(又は)排泄物のための貯蔵サイロ、そのサイロから 供給装置により燃焼装置へその材料が供給でき、前記燃焼装置からの燃焼ガスの 排出部に接続された熱交換器、及び燃焼ガスからの硫黄及び窒素の酸化物のため の熱交換器に接続された酸化カルシウム床を有する容器を有する。The invention also relates to a plant as described above, which plant comprises the method according to the invention. storage silos for manure and/or excrement treated in accordance with; A supply device can supply the material to the combustion device, and the combustion gas from the combustion device can be supplied with the material. Heat exchanger connected to the exhaust, and for oxides of sulfur and nitrogen from the combustion gases a vessel with a bed of calcium oxide connected to a heat exchanger.
本発明を、本発明による装置の好ましい態様に関する図面に関連して更に説明す る。The invention will be further explained in connection with the drawings of preferred embodiments of the device according to the invention. Ru.
第1図に関し、肥料貯槽1(肥料ピット又はサイロ)中に加熱管2が配備されて いる。肥料ビット上のガスはポンプ3により排出され、それらは洗浄装置4中に 底がら導入される。この装置には上方へ行く程粒径が減少する複数の充填単位装 置(unit)の層が入っている。これらの層の上に開口6が開けられた水平パ イプ5が配置されている。ポンプ16はこのパイプに水を供給し、その水は例え ば、最高lO℃の温度を有する。洗浄装置4には、底に溢流パイプが配備されて おり、それを通って、洗浄装置4の底に収集されたアンモニア及び硫化水素を含 む水溶液が水酸化鉄スラッジ床8中へ底がら導入される。そこで硫化水素は硫化 鉄に転化する。アンモニア溶液はこの床の上から排出され保存される。Regarding Fig. 1, heating pipe 2 is installed in fertilizer storage tank 1 (fertilizer pit or silo). There is. The gases on the fertilizer bits are pumped out by a pump 3 and they are transferred into a cleaning device 4. It will be introduced from the bottom up. The device has several packing units with particle size decreasing upwards. It contains layers of units. A horizontal pattern with openings 6 above these layers Type 5 is placed. Pump 16 supplies water to this pipe, and the water is e.g. For example, it has a temperature of up to 10°C. The cleaning device 4 is equipped with an overflow pipe at the bottom. and through it the ammonia and hydrogen sulfide-containing gas collected at the bottom of the cleaning device 4. An aqueous solution of the iron hydroxide sludge is introduced into the iron hydroxide sludge bed 8 from the bottom. So hydrogen sulfide is sulfurized Converts into iron. The ammonia solution is drained over this bed and stored.
アンモニア及び硫化水素が殆ど除かれているが、がなりの量のメタンガスを含む ガスが燃焼装置9に送られ、そこでメタンを燃焼する。炉が始動又は消える時、 ガスバーナー10を用いて温度を、炉を通過するガス中のメタンが発火し、その ガス中の酸素により燃焼するような温度へ上昇させることができる。燃焼ガスは 、大気中へ放出される前に、ビット1中の肥料を加熱するのに少なくとも部分的 に用いられる。このなめ、それらをパイプ20を通って貯槽lの加熱用管2へ送 る。もし望むならば、それらのガス中に存在するCO2を、水酸化カルシウム溶 液にそのガス流を通過させることにより結合させてもよい。Most of ammonia and hydrogen sulfide are removed, but a considerable amount of methane gas is included. The gas is sent to a combustion device 9 where the methane is combusted. When the furnace starts or turns off, Using the gas burner 10, the temperature is set so that the methane in the gas passing through the furnace ignites and The oxygen in the gas can raise the temperature to the point where it burns. The combustion gas , at least partially to heat the fertilizer in Bit 1 before being released into the atmosphere. used for. This lick sends them through the pipe 20 to the heating pipe 2 of the storage tank l. Ru. If desired, the CO2 present in those gases can be dissolved in calcium hydroxide. The combination may be made by passing the gas stream through the liquid.
本発明による装置の代表的な態様として、舎内空気もパイプ12によって排出し 、次にその空気を肥料ピットから排出されたガス流と一緒に洗浄装置4中に送る 。In a typical embodiment of the device according to the invention, indoor air is also exhausted through the pipe 12. , which air is then sent into the cleaning device 4 together with the gas stream discharged from the fertilizer pit. .
この舎内空気は、厩舎内に配置されたパーイブで、調節可能な吸引バルブがその 全長に互って取付けられたパイプ15を通って調節可能な扇風機13によって厩 舎から排出される。This indoor air is supplied by a perve located inside the stable, which is controlled by an adjustable suction valve. Stables are provided by adjustable fans 13 through pipes 15 attached to each other along the entire length. It is discharged from the building.
第2図は、上述した装置を変更したものに関し、その場合、パイプ12を通って 排出され、肥料貯槽がら取り出されたガスから分離された舎内空気を第二の洗浄 装置4aへ送る。両方の洗浄装置4及び4Aでは、上方へ移動するガスは再循環 アンモニア溶液により洗浄され、その溶液は、水酸化鉄スラッジ床が存在する地 中に配置されたタンク11からポンプ16により送り出される、床8は地下水又 は水道水によって冷却され、その水はパイプ29を通って送られる。FIG. 2 relates to a modification of the device described above, in which case the pipe 12 is A second cleaning of the indoor air separated from the gas discharged and extracted from the fertilizer storage tank Send to device 4a. In both cleaning devices 4 and 4A, the upwardly moving gas is recirculated. The solution is washed with an ammonia solution and the solution is applied to the ground where the iron hydroxide sludge bed is present. The floor 8 is filled with ground water or water pumped by a pump 16 from a tank 11 located inside. is cooled by tap water, which is sent through pipe 29.
第1図及び第2図の両方の炉9中には管27が配備されており、それを通って水 を流すことができ、出発材料の加熱以外の目的、例えば農場内の集中暖房のため に過剰に生成した熱を利用することができる。一方向性バルブ39a及び33a には、燃焼炉から炎が逆流しないように防止ガーゼが配置されている。第2図中 の分岐管25Aは、もし望むならば、パイプ25を通って排出された洗浄された ガスの一部分をガス発生器へ送っても良いことを例示している。A tube 27 is provided in the furnace 9 of both FIGS. 1 and 2, through which water is passed. can flow for purposes other than heating the starting material, e.g. for central heating within the farm. The excess heat generated can be used to One-way valves 39a and 33a A protective gauze is placed in the furnace to prevent flames from flowing back from the combustion furnace. In Figure 2 The branch pipe 25A of This example illustrates that a portion of the gas may be sent to a gas generator.
パイプ20中には制御バルブ28が配備されており、貯槽1中の熱の必要量に従 って調節される。燃焼室9中のガス混合物の組成は、制御バルブ30によって調 節することができる。A control valve 28 is provided in the pipe 20 to control the amount of heat required in the storage tank 1. It is adjusted. The composition of the gas mixture in the combustion chamber 9 is regulated by a control valve 30. It can be divided into sections.
第3図は、第1図及び第2図の装置を更に発展させたもので、燃焼炉9中で過剰 の肥料を燃焼することができるようにしたものに関する。Fig. 3 shows a further development of the apparatus shown in Figs. 1 and 2, in which excess Contains fertilizers that can be burned.
このプラントでは、過剰の肥料を収集容器21中に入れる。肥料ピット1(第1 図及び第2図)中で本発明の方法に従い処理されたこの肥料は、約30重量%の 水分含有量を有する。肥料ピット1中では二つの層が形成され、加熱によってメ タン及び他のガスが引き出された後、上の層は約70重量%の固形物含有量を有 する。肥料ビット中の燐酸塩の大部分はこれら上の層中で終わっている。In this plant, excess fertilizer is placed in a collection container 21. Fertilizer pit 1 (1st This fertilizer treated according to the method of the invention in Figs. It has a moisture content. Two layers are formed in the fertilizer pit 1, and the fertilizer is heated. After the tunic and other gases are drawn off, the top layer has a solids content of about 70% by weight. do. Most of the phosphate in the fertilizer bit ends up in these upper layers.
下のもっと液体状の層は燐酸塩含有量が遥かに少なく、最終的にはそれを脱燐し た後排出される。The lower, more liquid layer has much less phosphate and will eventually dephosphorize it. It is then discharged.
燐酸塩含有量の遥かに高い上の層が直接地面に肥料として用いられない限り、そ れを容器21中に運び込む。この容器から乾燥肥料を運搬機22により燃焼炉9 中に導入する。肥料の鉱物残渣は灰として炉の底にある火格子22を通って落下 する。これらの灰は燐酸塩及び珪酸塩からなる。燃焼炉9中での肥料の燃焼によ り、硫黄酸化物及び窒素酸化物も生成する。環境に対して非常に有害なことにな るこれらの酸化物が大気中へ流出するのを防ぐために、硫黄及び窒素の酸化物を 含有する高温燃焼ガスを酸化カルシウムの床17に通す。この酸化カルシウムは 硫黄及び窒素の酸化物を燐酸カルシウム及び硝酸塩カルシウムへ転化する。熱回 収装置18及び塵フィルター19が燃焼炉9と酸化カルシウム床17の間に配置 されている。熱交換器中では循環水が加熱され、炉9からの燃焼ガスが冷却され る。酸化カルシウム床の下の塵フィルター19中で、塵は燃焼ガスから除去され 、然る後、このガスは酸化カルシウム床19を通過する。もし望むならば、床1 9の酸化カルシウムは石灰石(CaC○、)をか焼することにより生成させるこ とができる。その場合、例えば水軟水化装置から生じたカルサイト粒子(僅か0 .5%の水しか含まないCa CO* )を−、燃焼すべき肥料と一緒に類9中 に導入することができる。これらの粒子は炉中に行き亙っている高温でか焼され る。形成されたCaOを、炉底中の肥料鉱物成分と一緒に収集する。CaO、燐 酸塩及び珪酸塩の混合物は、燃焼ガス中の硫黄及び窒素の酸化物を結合するため の床I9に用いることができる。これはCaOを燐酸カルシウム及び硝酸カルシ ウムに転化する結果になる。燐酸塩、Vl、酸塩、硝酸塩、及びカルシウム生成 物の混合物は肥料として用いてもよい。Unless the upper layer, which has a much higher phosphate content, is applied directly to the ground as fertilizer, This is carried into the container 21. The dry fertilizer is transferred from this container to a combustion furnace 9 by a transporter 22. Introduce it inside. The mineral residues of the fertilizer fall as ash through the grate 22 at the bottom of the furnace. do. These ashes consist of phosphates and silicates. By burning the fertilizer in the combustion furnace 9 Sulfur oxides and nitrogen oxides are also produced. very harmful to the environment oxides of sulfur and nitrogen to prevent these oxides from escaping into the atmosphere. The hot combustion gases contained therein are passed through a bed 17 of calcium oxide. This calcium oxide Converts sulfur and nitrogen oxides to calcium phosphate and calcium nitrate. heat cycle A collection device 18 and a dust filter 19 are arranged between the combustion furnace 9 and the calcium oxide bed 17. has been done. In the heat exchanger, the circulating water is heated and the combustion gas from the furnace 9 is cooled. Ru. Dust is removed from the combustion gases in a dust filter 19 below the calcium oxide bed. , after which this gas passes through a bed of calcium oxide 19. floor 1 if you want Calcium oxide in No. 9 can be produced by calcining limestone (CaC○,). I can do it. In that case, for example, calcite particles (only 0 .. Ca CO*), which contains only 5% water, is combined with the fertilizer to be burned in Category 9. can be introduced into These particles are calcined at high temperatures prevailing in the furnace. Ru. The formed CaO is collected together with the fertilizer mineral components in the hearth bottom. CaO, phosphorus Mixtures of acid salts and silicates to bind sulfur and nitrogen oxides in the combustion gases It can be used for floor I9. This converts CaO into calcium phosphate and calcium nitrate. This results in conversion to um. Phosphate, Vl, acid salt, nitrate, and calcium production The mixture may be used as a fertilizer.
第3図によるプラントでは、熱交換器中で加熱された水は、導管20を通ってサ イロ1中の加熱用管中へ送られ(第1図及び第2図参照)、その中の肥料を加熱 し、更に、例えば集中暖房装置30又はボイラー31の加熱に用いてもよい。In the plant according to FIG. 3, the water heated in the heat exchanger passes through conduit 20 to the The fertilizer is sent to the heating pipe in Iro 1 (see Figures 1 and 2) and heats the fertilizer inside. However, it may also be used, for example, to heat a central heating device 30 or a boiler 31.
洗浄塔から来たCH,ガスもガス発生器の燃焼機関24のために用いる場合には 、導管25を通って供給されたこのCH4ガスを、厩舎から取り出され、洗浄塔 で洗浄され、導管26を経て供給されたC H4+ 02 + N 2のガス混 合物と、ガス発生器のタービンの金属がそのガス流中の窒素酸化物によって腐食 されるのを防ぐなめ、予め混合することはしない。When CH and gas coming from the cleaning tower are also used for the combustion engine 24 of the gas generator, , this CH4 gas supplied through conduit 25 is taken out from the stable and sent to the washing tower. The gas mixture of C H4 + 02 + N2 supplied via conduit 26 metals in the gas generator turbine are corroded by nitrogen oxides in the gas stream. Do not pre-mix to prevent licking.
国際調査報告international search report
Claims (12)
Applications Claiming Priority (2)
Application Number | Priority Date | Filing Date | Title |
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NL8902068A NL8902068A (en) | 1989-08-15 | 1989-08-15 | METHOD AND APPARATUS FOR PROCESSING MATERIALS, WHICH MAY CAUSE METHANE ESCAPE AND ENVIRONMENTALLY HARMFUL SUBSTANCES |
NL8902068 | 1989-08-15 |
Publications (1)
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JPH04507217A true JPH04507217A (en) | 1992-12-17 |
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JP2511502A Pending JPH04507217A (en) | 1989-08-15 | 1990-08-15 | Methods and apparatus for treating materials from which methane and other chemicals harmful to the environment are released |
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EP (1) | EP0487574A1 (en) |
JP (1) | JPH04507217A (en) |
KR (1) | KR920703183A (en) |
CN (1) | CN1050826A (en) |
AU (1) | AU6162490A (en) |
CA (1) | CA2064698A1 (en) |
DD (1) | DD298068A5 (en) |
NL (1) | NL8902068A (en) |
WO (1) | WO1991002582A1 (en) |
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
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JP2002361200A (en) * | 2001-06-07 | 2002-12-17 | Ishikawajima Harima Heavy Ind Co Ltd | Deodorization treatment system |
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MY143253A (en) | 2002-08-01 | 2011-04-15 | Gfe Patent As | Method and device for stripping ammonia from liquids |
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DE3709521A1 (en) * | 1986-05-06 | 1987-11-12 | Ilka Luft & Kaeltetechnik | Process and device for combined purification of flue gas and animal house air |
NL8602150A (en) * | 1986-08-25 | 1988-03-16 | Grontmij N V | Removing sulphur cpds. from air over waste water - by spraying with water to remove part into the waste water and then passing through a carrier contg. microorganisms |
-
1989
- 1989-08-15 NL NL8902068A patent/NL8902068A/en not_active Application Discontinuation
-
1990
- 1990-08-14 DD DD90343448A patent/DD298068A5/en not_active IP Right Cessation
- 1990-08-15 AU AU61624/90A patent/AU6162490A/en not_active Abandoned
- 1990-08-15 JP JP2511502A patent/JPH04507217A/en active Pending
- 1990-08-15 EP EP19900912224 patent/EP0487574A1/en not_active Withdrawn
- 1990-08-15 KR KR1019920700324A patent/KR920703183A/en not_active Withdrawn
- 1990-08-15 CN CN90107583A patent/CN1050826A/en active Pending
- 1990-08-15 WO PCT/NL1990/000116 patent/WO1991002582A1/en not_active Application Discontinuation
- 1990-08-15 CA CA 2064698 patent/CA2064698A1/en not_active Abandoned
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
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JP2002361200A (en) * | 2001-06-07 | 2002-12-17 | Ishikawajima Harima Heavy Ind Co Ltd | Deodorization treatment system |
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CN1050826A (en) | 1991-04-24 |
KR920703183A (en) | 1992-12-17 |
DD298068A5 (en) | 1992-02-06 |
WO1991002582A1 (en) | 1991-03-07 |
NL8902068A (en) | 1991-03-01 |
AU6162490A (en) | 1991-04-03 |
EP0487574A1 (en) | 1992-06-03 |
CA2064698A1 (en) | 1991-02-16 |
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