JP6328901B2 - Method for producing solid fuel and solid fuel - Google Patents

Method for producing solid fuel and solid fuel Download PDF

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JP6328901B2
JP6328901B2 JP2013205213A JP2013205213A JP6328901B2 JP 6328901 B2 JP6328901 B2 JP 6328901B2 JP 2013205213 A JP2013205213 A JP 2013205213A JP 2013205213 A JP2013205213 A JP 2013205213A JP 6328901 B2 JP6328901 B2 JP 6328901B2
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solid fuel
biomass
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fuel
pulverized
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JP2015067789A (en
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宏 新倉
宏 新倉
友紀 川真田
友紀 川真田
小野 裕司
裕司 小野
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Nippon Paper Industries Co Ltd
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    • YGENERAL 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
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02EREDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
    • Y02E50/00Technologies for the production of fuel of non-fossil origin
    • Y02E50/10Biofuels, e.g. bio-diesel
    • YGENERAL 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
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02EREDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
    • Y02E50/00Technologies for the production of fuel of non-fossil origin
    • Y02E50/30Fuel from waste, e.g. synthetic alcohol or diesel

Description

本発明は、木質系バイオマスを焙焼(torrefaction)することによって得られる、塩素含有率が低い固体燃料、及び固体燃料の製造方法に関する。   The present invention relates to a solid fuel having a low chlorine content obtained by torrefaction of woody biomass and a method for producing the solid fuel.

近年、化石燃料の枯渇化及びCO排出による地球温暖化への対策として、バイオマスを原料とする燃料の利用が検討されている。一般にバイオマスとは、エネルギー源又は工業原料として利用することのできる生物体をいい、代表的なものは木材、建築廃材、農産廃棄物等である。従来よりバイオマスを有効利用する方法が各種提案されている。その中でも、バイオマスを低コストで以って高付加価値物に転換できる有用な方法として、バイオマスを炭化して固体燃料を製造する方法がある。これは、バイオマスを炭化炉に投入して酸素欠乏雰囲気下で所定時間加熱して炭化処理し、固体燃料を製造するものである。 In recent years, as a countermeasure against global warming due to depletion of fossil fuels and CO 2 emissions, the use of fuels made from biomass has been studied. In general, biomass refers to a living organism that can be used as an energy source or an industrial raw material, and representative examples are wood, building waste, agricultural waste, and the like. Various methods for effectively utilizing biomass have been proposed. Among them, as a useful method capable of converting biomass into a high value-added product at a low cost, there is a method for producing a solid fuel by carbonizing biomass. In this method, biomass is put into a carbonization furnace and heated for a predetermined time in an oxygen-deficient atmosphere to be carbonized to produce a solid fuel.

このようにして製造された固体燃料は、発電設備や焼却設備等の燃焼設備の燃料に用いられるが、この場合、燃焼効率を向上させるために固体燃料を細かく粉砕して微粉燃料として用いることがある。固体燃料は単独であるいは石炭と混合して粉砕されるが、バイオマスのうち木質系バイオマスは大部分が繊維質であるため、粉砕性が悪く、燃焼効率の低下、粉砕機の運転性低下等の問題があった。   The solid fuel thus produced is used as a fuel for combustion facilities such as power generation facilities and incineration facilities. In this case, the solid fuel may be finely pulverized and used as a finely divided fuel in order to improve combustion efficiency. is there. Solid fuel is pulverized alone or mixed with coal, but most of wood biomass is fibrous, so the pulverization is poor, the combustion efficiency decreases, the operability of the pulverizer decreases, etc. There was a problem.

特許文献1には、材廃材、間伐材、庭木、建築廃材等の木質系バイオマスを240℃以上300℃以下の温度で、15分以上90分以下の時間で熱分解した後に粉砕する方法が開示されている。加熱温度が240℃より低い温度であると破砕性、粉砕性が向上せず、300℃よりも高い温度であると破砕、粉砕時にサブミクロンオーダーの微粉量が増大して粉体トラブルを生じ易くなるため好ましくないとしている。   Patent Document 1 discloses a method of pulverizing woody biomass such as wood waste, thinned wood, garden wood, building waste, etc., at a temperature of 240 ° C. or higher and 300 ° C. or lower for 15 minutes or longer and 90 minutes or shorter. Has been. If the heating temperature is lower than 240 ° C, crushability and pulverization will not be improved. If the heating temperature is higher than 300 ° C, the amount of fine powder on the order of submicron will increase during crushing and pulverization, and powder troubles will easily occur. Therefore, it is not preferable.

また、特許文献2には穀類、実、種子を含むバイオマスを酸素濃度1〜5%、処理温度350〜400℃で30〜90分加熱して炭化処理することで、石炭と同等の粉砕性を有する固体燃料を製造する方法が開示されている。   Patent Document 2 discloses that biomass containing cereals, berries and seeds is carbonized by heating for 30 to 90 minutes at an oxygen concentration of 1 to 5% and a treatment temperature of 350 to 400 ° C. A method for producing a solid fuel having the same is disclosed.

塩素化合物が含まれているバイオマスから得られる固体燃料は塩素含有率が高く、このような固体燃料は燃焼設備の腐食に対する対策や排ガス処理設備が必要となる。従って、固体燃料の塩素含有率を低減させることが求められる。特許文献3には、バイオマスを含む原料から焙焼によって製造される固体燃料の塩素含有率を低下させるために、固体燃料を水で洗浄する方法が開示されている。   Solid fuels obtained from biomass containing chlorine compounds have a high chlorine content, and such solid fuels require measures against corrosion of combustion facilities and exhaust gas treatment facilities. Therefore, it is required to reduce the chlorine content of the solid fuel. Patent Document 3 discloses a method of washing a solid fuel with water in order to reduce the chlorine content of the solid fuel produced by roasting from a raw material containing biomass.

特開2006−26474号公報JP 2006-26474 A 特開2009−191085号公報JP 2009-191085 特表2009−540097号公報Special Publication 2009-540097

しかしながら、塩素化合物が含まれているバイオマスから得られる固体燃料は、塩素含有率が高く、ボイラーの燃料として使用することが困難である。従って、塩素含有率を低減するための後処理や、燃焼設備の腐食に対する対策や排ガス処理設備が必要となるが、コストアップなる。   However, solid fuels obtained from biomass containing chlorine compounds have a high chlorine content and are difficult to use as boiler fuel. Therefore, post-treatment for reducing the chlorine content, countermeasures against corrosion of combustion equipment, and exhaust gas treatment equipment are required, but the cost increases.

本発明者等は、上記課題を解決するため鋭意検討した結果、木質系バイオマスを酸素濃度10%以下で、かつ炉内温度250〜500℃の条件下で焙焼(torrefaction)することによって、塩素含有率が0.002%以下である固体燃料を効率よく製造できることを見出した。   As a result of intensive studies to solve the above-mentioned problems, the present inventors have chlorinated woody biomass under the conditions of an oxygen concentration of 10% or less and a furnace temperature of 250 to 500 ° C., thereby producing chlorine. It has been found that a solid fuel having a content of 0.002% or less can be produced efficiently.

本発明によれば、木質系バイオマスを特定の温度範囲で焙焼することにより、洗浄等の特別な処理を行わなくても塩素含有率の低い固体燃料を効率よく製造できる。また、本発明の製造方法にて得られる固形燃料は、物質収率、熱量収率が高く、さらに石炭と同等の粉砕性を有し、高密度であるため、石炭と混合して粉砕処理して微粉炭ボイラーの燃料として高い比率で混炭して使用することできる。   According to the present invention, a solid fuel having a low chlorine content can be efficiently produced without roasting woody biomass in a specific temperature range without performing special treatment such as washing. In addition, the solid fuel obtained by the production method of the present invention has a high substance yield and a calorie yield, and has a pulverization property equivalent to that of coal and a high density. As a fuel for pulverized coal boilers, it can be used by mixing at a high ratio.

本発明において、原料として木質系バイオマスを使用する。木質系バイオマスとしては、木材チップ、樹皮(バーク)、おが屑、鋸屑等が挙げられる。これらの木質系バイオマスはあまり利用されることなく、廃棄されることが多いのが現状である。樹種は広葉樹、針葉樹のいずれも使用できる。   In the present invention, woody biomass is used as a raw material. Woody biomass includes wood chips, bark, sawdust, sawdust and the like. At present, these woody biomass is not often used and is often discarded. The tree species can be either hardwood or softwood.

本発明において、木質系バイオマスは0.1〜100mmのサイズに粉砕された粉砕物を使用することが好ましく、0.1〜50mmのサイズのものを使用することがさらに好ましい。なお、本発明において、木質系バイオマス粉砕物のサイズとは、篩い分け器の円形の穴の大きさによって篩い分けされたものである。木質系バイオマスを粉砕するための装置としては、ナイフ切削型バイオマス燃料用チッパーで粉砕処理することが好ましい。   In the present invention, the woody biomass is preferably a pulverized product pulverized to a size of 0.1 to 100 mm, more preferably 0.1 to 50 mm. In the present invention, the size of the pulverized woody biomass is obtained by sieving according to the size of the circular hole of the sieving device. As an apparatus for pulverizing the woody biomass, it is preferable to pulverize with a knife cutting type biomass fuel chipper.

本発明において、木質系バイオマスは高密度化することが好ましい。本発明における高密度化とは、木質系バイオマス粉砕物をブリケットやペレット状に成型する処理のことを意味する。成型処理を行うことによって、嵩密度を大幅に高めることができる。高密度化する前の木質系バイオマス粉砕物の嵩密度は0.01g/cm〜0.3g/cm程度であるが、高密度化処理後の嵩密度は0.55g/cm〜1.0g/cmである。 In the present invention, the woody biomass is preferably densified. Densification in the present invention means a process of forming a pulverized woody biomass into briquettes or pellets. By performing the molding process, the bulk density can be significantly increased. Although the bulk density before woody pulverized biomass densifying is about 0.01g / cm 3 ~0.3g / cm 3 , the bulk density after densification is 0.55 g / cm 3 to 1 0.0 g / cm 3 .

高密度化処理後の木質系バイオマス粉砕物の嵩密度は、0.55g/cm以上とすることが好ましく、0.6g/cm以上にすることがさらに好ましい。嵩密度が0.55g/cm未満であると固体燃料を燃料として微粉炭ボイラーで燃焼させる際、微粉炭ミルの粉砕室中の容積が大きくなり、粉砕室からこぼれ落ちるため、石炭との混合比率をあまり大きくすることが不可能なため、本発明の効果を最大限に得ることができない。 The bulk density of the pulverized woody biomass after the densification treatment is preferably 0.55 g / cm 3 or more, and more preferably 0.6 g / cm 3 or more. When the bulk density is less than 0.55 g / cm 3 , the volume in the grinding chamber of the pulverized coal mill increases when the solid fuel is burned with the fuel as fuel and spills out of the grinding chamber. Since the ratio cannot be increased too much, the effect of the present invention cannot be obtained to the maximum.

本発明における高密度化を行う前に、樹皮粉砕物の水分を10〜50%とすることが望ましい。水分が10%より少ないとブリケッターやペレタイザーの内部で閉塞が発生し、安定した成型物の製造ができない。水分が50%を超えると成型できず、粉体状またはペースト状で排出される。   Before densification in the present invention, it is desirable that the water content of the bark pulverized product is 10 to 50%. If the water content is less than 10%, clogging occurs inside the briquetter or pelletizer, and a stable molded product cannot be produced. If the water content exceeds 50%, it cannot be molded and is discharged in the form of powder or paste.

本発明において、木質系バイオマス100質量部に対してバインダーを0〜50質量部添加してもよい。バインダーは特に限定されていないが、有機高分子(リグニンなど)、無機高分子(アクリル酸アミドなど)、農業残渣(ふすま(小麦粉製造時に発生する残渣)など)等が望ましい。木質系バイオマスを効率よく有効利用することを目的としている観点から、バインダー添加部数は少ない方が望ましく、木質系バイオマス100質量部に対して0〜50質量部、より好ましくは0〜20質量部が望ましい。ただし、50質量部以上添加しても高密度化が不可能であるというわけではない。   In this invention, you may add 0-50 mass parts of binders with respect to 100 mass parts of woody biomass. The binder is not particularly limited, but an organic polymer (such as lignin), an inorganic polymer (such as acrylic amide), an agricultural residue (such as bran (residue generated during the production of wheat flour)) and the like are desirable. From the viewpoint of efficiently using woody biomass efficiently, it is desirable that the number of added parts of the binder is small, and 0 to 50 parts by weight, more preferably 0 to 20 parts by weight with respect to 100 parts by weight of woody biomass. desirable. However, even if 50 parts by mass or more is added, it is not impossible to increase the density.

本発明において高密度化処理を行うための装置は特に限定されていないが、ブリケッター(北川鉄工所(株)製)、リングダイ式ペレタイザー(CPM(株)製、(株)御池鉄工所製)、フラットダイ式ペレタイザー(ダルトン(株)製)等が望ましい。   In the present invention, the apparatus for performing the densification treatment is not particularly limited, but a briquetter (made by Kitagawa Iron Works Co., Ltd.), a ring die type pelletizer (made by CPM Co., Ltd., made by Miike Iron Works Co., Ltd.) A flat die type pelletizer (manufactured by Dalton Co., Ltd.) is desirable.

本発明における焙焼(torrefaction)とは、低酸素雰囲気下で、所謂炭化処理よりも低い温度で加熱する処理のことである。通常の木材の炭化処理の温度は400〜1200℃であるが、焙焼はより低い温度で行われる。焙焼を行うことによって、その出発原料よりも高いエネルギー密度を有する固体燃料が得られる。   The torrefaction in the present invention is a process of heating in a low oxygen atmosphere at a temperature lower than a so-called carbonization process. The normal carbonization temperature of wood is 400-1200 ° C., but roasting is performed at a lower temperature. By performing the roasting, a solid fuel having an energy density higher than that of the starting material can be obtained.

本発明における焙焼の処理条件は、酸素濃度10%以下で、炉内温度250〜500℃である。酸素濃度が10%を超えると物質収率、熱量収率が低下する。また、炉内温度が250℃未満では、塩素含有率を低減させることが不十分となり、後述する粉砕性が不十分である。炉内温度が500℃を超えた場合は、塩素含有率の低減が頭打ちとなる。また、温度が350℃を超えると、物質収率、熱量収率の低下が顕著になる。従って、物質収率、熱量収率も勘案すると、炉内温度は250〜400℃が好ましく、さらに260〜350℃がさらに好ましい。ヘミセルロースは270℃付近で熱分解が顕著になるのに対して、セルロースは355℃付近、リグニンは365℃付近で熱分解が顕著になるので、焙焼の処理温度を170〜350℃とすることで、ヘミセルロースを優先的に熱分解して、物質収率と粉砕性を両立できる固体燃料を製造することが可能になると推察される。   The treatment conditions for roasting in the present invention are an oxygen concentration of 10% or less and a furnace temperature of 250 to 500 ° C. When the oxygen concentration exceeds 10%, the substance yield and the calorie yield are lowered. Moreover, when the furnace temperature is less than 250 ° C., it is insufficient to reduce the chlorine content, and the grindability described later is insufficient. When the furnace temperature exceeds 500 ° C., the reduction of the chlorine content reaches its peak. Moreover, when temperature exceeds 350 degreeC, the fall of a substance yield and a calorific value yield will become remarkable. Therefore, considering the substance yield and the heat yield, the furnace temperature is preferably 250 to 400 ° C, more preferably 260 to 350 ° C. Hemicellulose is prone to thermal decomposition at around 270 ° C, whereas cellulose is prone to thermal decomposition at around 355 ° C, and lignin is prominent at around 365 ° C. Thus, it is speculated that hemicellulose can be preferentially pyrolyzed to produce a solid fuel that can achieve both material yield and pulverization.

本発明において、焙焼処理を行うための装置は特に限定されないが、ロータリーキルン、竪型炉が好ましい。なお、酸素濃度を10%以下に調整するため装置内を窒素等の不活性ガスで置換することが好ましい。処理時間は1〜180分が好ましく、1〜60分がさらに好ましい。また、焙焼処理を行うための装置として、外熱式ロータリーキルンを使用してもよい。外熱式ロータリーキルンとは、キルン内筒の一部または全部をキルン外筒で覆う構造を有するもので、内筒内で木質系バイオマスの焙焼を行い、外筒内で燃料を燃焼させて内筒内部の木質系バイオマスを間接的に加熱する。   In the present invention, the apparatus for performing the roasting treatment is not particularly limited, but a rotary kiln and a vertical furnace are preferable. In order to adjust the oxygen concentration to 10% or less, the inside of the apparatus is preferably replaced with an inert gas such as nitrogen. The treatment time is preferably 1 to 180 minutes, more preferably 1 to 60 minutes. Moreover, you may use an external heating type rotary kiln as an apparatus for performing a roasting process. An externally heated rotary kiln has a structure in which part or all of the kiln inner cylinder is covered with the kiln outer cylinder. The wood biomass is roasted in the inner cylinder, and fuel is burned in the outer cylinder. The woody biomass inside the cylinder is indirectly heated.

本発明で得られる固体燃料は、原料の木質バイオマスに対して物質収率で60〜95%、熱量収率で70〜95%である。また、粉砕性の指標であるJIS M 8801:2004に規定のハードグローブ粉砕性指数(HGI)は30以上が好ましく、40以上がさらに好ましい。HGIが高くなるほど、粉砕され易いことを示している。HGIが30〜70の範囲であれば、石炭と混合して粉砕処理することが可能となる。石炭のHGIは通常40〜70であるので、本発明で得られた固体燃料は石炭と同等の粉砕性を有している。   The solid fuel obtained by the present invention has a material yield of 60 to 95% and a calorific yield of 70 to 95% with respect to the raw woody biomass. The hard glove grindability index (HGI) defined in JIS M 8801: 2004, which is an index of grindability, is preferably 30 or more, and more preferably 40 or more. It shows that it becomes easy to grind, so that HGI becomes high. If HGI is in the range of 30 to 70, it can be mixed with coal and pulverized. Since the HGI of coal is usually 40 to 70, the solid fuel obtained in the present invention has the same pulverizability as coal.

以下に実施例にて本発明を詳細に説明するが、本発明はこれらに限定されるものではない。   EXAMPLES The present invention will be described in detail below with reference to examples, but the present invention is not limited to these examples.

[実施例1]
ユーカリのチップをナイフ切削型バイオマス燃料用チッパー(緑産(株)製、Wood Hacker MEGA360DL)にて粉砕処理した。粉砕後、70mmのスクリーンを通過した樹皮粉砕物を原料として、乾燥機で120℃、10分間乾燥処理を行った。得られた生成物の水分を12%に調整し、リングダイ式ペレタイザー((株)御池鉄工所製、MIIKE多目的造粒機ペレットミルSPM−500型)にてダイ穴直径6mm、ダイ厚さ36mmのリングダイを用いて高密度化処理を行い、嵩密度0.60g/cmのペレットを得た。続いてこのペレットを原料として、小型キルン型炭化炉を用い、窒素パージして(酸素濃度1%未満)、炉内温度260℃、滞留時間30分で焙焼を行って固体燃料を得た。
[Example 1]
Eucalyptus chips were pulverized with a knife cutting type biomass fuel chipper (Wood Hacker MEGA360DL, manufactured by Green Products Co., Ltd.). After pulverization, the bark pulverized material that passed through a 70 mm screen was used as a raw material, and a drying treatment was performed at 120 ° C. for 10 minutes using a dryer. The water content of the obtained product was adjusted to 12%, and the die hole diameter was 6 mm and the die thickness was 36 mm using a ring die pelletizer (MIIKE Multipurpose Granulator Pellet Mill SPM-500, manufactured by Miike Iron Works Co., Ltd.). Density treatment was performed using a ring die to obtain pellets with a bulk density of 0.60 g / cm 3 . Subsequently, using this pellet as a raw material, using a small kiln type carbonization furnace, nitrogen purge (oxygen concentration of less than 1%), and roasting was performed at a furnace temperature of 260 ° C. and a residence time of 30 minutes to obtain a solid fuel.

[実施例2]
炉内温度を280℃とした以外は、実施例1と同様にして固体燃料を得た。
[Example 2]
A solid fuel was obtained in the same manner as in Example 1 except that the furnace temperature was 280 ° C.

[実施例3]
炉内温度を300℃とした以外は、実施例1と同様にして固体燃料を得た。
[Example 3]
A solid fuel was obtained in the same manner as in Example 1 except that the furnace temperature was 300 ° C.

[実施例4]
炉内温度を500℃とした以外は、実施例1と同様にして固体燃料を得た。
[Example 4]
A solid fuel was obtained in the same manner as in Example 1 except that the furnace temperature was 500 ° C.

[比較例1]
実施例1で調製したペレットを焙焼処理を行わないで固体燃料とした。
[Comparative Example 1]
The pellet prepared in Example 1 was used as a solid fuel without being roasted.

[比較例2]
炉内温度を200℃とした以外は、実施例1と同様にして固体燃料を得た。
[Comparative Example 2]
A solid fuel was obtained in the same manner as in Example 1 except that the furnace temperature was 200 ° C.

[比較例3]
炉内温度を240℃とした以外は、実施例1と同様にして固体燃料を得た。
[Comparative Example 3]
A solid fuel was obtained in the same manner as in Example 1 except that the furnace temperature was 240 ° C.

[比較例4]
炉内温度を600℃とした以外は、実施例1と同様にして固体燃料を得た。
[Comparative Example 4]
A solid fuel was obtained in the same manner as in Example 1 except that the furnace temperature was 600 ° C.

実施例1〜4、比較例1〜4で得られた生成物について下記の項目について評価し、結果を表1に示した。
・塩素含有率:JIS Z 7302−6に従い、塩素濃度をイオンクロマトグラフィーで測定し、これを基に算出した。
・物質収率:焙焼前後の試料の重量から計算した。
The following items were evaluated for the products obtained in Examples 1 to 4 and Comparative Examples 1 to 4, and the results are shown in Table 1.
Chlorine content: Chlorine concentration was measured by ion chromatography according to JIS Z 7302-6 and calculated based on this.
Material yield: calculated from the weight of the sample before and after roasting.

Figure 0006328901
Figure 0006328901

表1に示されるように、実施例1〜4の固体燃料は、塩素含有率が0.002%以下であった。特に、実施例1、2は物質収率も高かった。これに対して、比較例1〜4では塩素含有率が0.002%を超えていた。   As shown in Table 1, the solid fuels of Examples 1 to 4 had a chlorine content of 0.002% or less. In particular, Examples 1 and 2 also had a high substance yield. On the other hand, in Comparative Examples 1 to 4, the chlorine content exceeded 0.002%.

Claims (2)

0.1〜100mmのサイズのユーカリの粉砕物嵩密度0.55g/cm 〜1,0g/cm となるように高密化処理し、酸素濃度10%以下で、かつ炉内温度250〜350℃の条件下で焙焼して得られる、JIS Z 7302−6に従って測定された塩素含有率が0.002%以下である固体燃料。 The pulverized size eucalyptus 0.1~100mm treated densified such that the bulk density 0.55g / cm 3 ~1,0g / cm 3 , an oxygen concentration of 10% or less, and the furnace temperature 250 A solid fuel having a chlorine content of 0.002% or less, measured according to JIS Z 7302-6, obtained by roasting at 350 ° C. 0.1〜100mmのサイズのユーカリの粉砕物嵩密度0.55g/cm 〜1,0g/cm となるように高密化処理し、酸素濃度10%以下で、かつ炉内温度250〜350℃の条件下で焙焼することを特徴とする、JIS Z 7302−6に従って測定された塩素含有率が0.002%以下である固体燃料の製造方法。 The pulverized size eucalyptus 0.1~100mm treated densified such that the bulk density 0.55g / cm 3 ~1,0g / cm 3 , an oxygen concentration of 10% or less, and the furnace temperature 250 A method for producing a solid fuel having a chlorine content measured according to JIS Z 7302-6 of 0.002% or less, characterized by roasting under conditions of 350 ° C.
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