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JP6401144B2 - Wood smoke treatment equipment - Google Patents
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JP6401144B2 - Wood smoke treatment equipment - Google Patents

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JP6401144B2
JP6401144B2 JP2015211364A JP2015211364A JP6401144B2 JP 6401144 B2 JP6401144 B2 JP 6401144B2 JP 2015211364 A JP2015211364 A JP 2015211364A JP 2015211364 A JP2015211364 A JP 2015211364A JP 6401144 B2 JP6401144 B2 JP 6401144B2
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彰 宮内
彰 宮内
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Description

本発明は、木材の防虫加工のための燻煙処理に関する。   The present invention relates to a soot treatment for insect repellent processing of wood.

従来から、防虫の目的で木材を燻煙処理することが行われている。建築用の木材に求められる安全性を考慮すると化学薬品を使用しない方法が好ましく、燻煙処理が有効な手段であることが知られている。   Conventionally, smoking treatment of wood has been performed for the purpose of insect control. Considering the safety required for building wood, a method that does not use chemicals is preferable, and it is known that smoke treatment is an effective means.

古来より煙の効果は良く知られており、たとえば富山県南砺市の五箇山の合掌づくりの家では、囲炉裏から昇る煙が2階、3階の骨組みや竹にしみ込み、表面が黒光りし、それらの骨組みのひとつひとつが何十年何百年と家を支えている。本願発明はこの煙の防虫効果を利用するものである。   The effect of smoke has been well known since ancient times. For example, in the Gokayama gassho-made house in Nanto City, Toyama Prefecture, smoke rising from the hearth soaks into the 2nd and 3rd floor frames and bamboo, and the surface glows black. Each of the frameworks has supported the house for decades and hundreds. The present invention utilizes this insect repellent effect.

特許文献1には、木材を燻煙処理して防蟻性能、防腐性能を付加した木材が記載されている。また、特許文献2には、木材に燻煙乾燥処理を施した後、鉄分を主成分とする木材保護剤と木酢液と木タールとの混合液に浸漬する防腐・防蟻処理方法が記載されている。特許文献3には、木材を燻煙処理した後に薬液を注入し防腐・防蟻処理をする方法が記載されている。   Patent Document 1 describes wood that has been treated with smoke to add ant-proofing performance and antiseptic performance. Patent Document 2 describes an antiseptic / anticidal treatment method in which wood is subjected to a smoke drying treatment and then immersed in a mixed solution of a wood protective agent mainly composed of iron, wood vinegar, and wood tar. ing. Patent Document 3 describes a method for preserving and preventing ant processing by injecting a chemical solution after smoking the wood.

特開2001―71305号公報JP 2001-71305 A 特開2005―324524号公報JP 2005-324524 A 特開2006―334913号公報JP 2006-334913 A

前記特許文献1に記載の発明においては、燻煙処理の後に当該木材をあらためて成形加工する必要がある。これは燻煙処理工程において木材の乾燥も行われるため当該木材が変形してしまうからである。これによりせっかく表面に施した燻煙処理部分を、燻煙処理後の成形加工において除去することとなり、その燻煙処理の効果が減少することは避けられない。   In the invention described in Patent Document 1, it is necessary to reshape the wood after the smoke treatment. This is because the wood is deformed because the wood is also dried in the smoke treatment process. As a result, the smoke treated portion applied to the surface is removed in the molding process after the smoke treatment, and it is inevitable that the effect of the smoke treatment is reduced.

また、前記特許文献2及び3に記載の発明では、燻煙処理の後に鉄分を主成分とする木材保護剤と木酢液と木タールとの混合液に浸漬したり、薬液を注入したりする必要があるため、工程が多く大きな手間がかかり、専用の装置が必要となり、さらに混合液や薬液などにかかるコスト負担も大きなものである。   Further, in the inventions described in Patent Documents 2 and 3, it is necessary to immerse in a mixed solution of a wood protective agent mainly composed of iron, wood vinegar, and wood tar or to inject a chemical after the smoke treatment. For this reason, there are many steps, a lot of time and effort are required, a dedicated device is required, and the cost burden on the liquid mixture or chemical solution is also large.

そこで、本願発明においては燻煙処理の後に成形加工などを必要とせず、そのまま使用できる状態にするという課題を解決するものであり、さらに燻煙処理工程のみであり、前記混合液や薬液など他の工程を必要としないで、低コストに防蟻・防腐処理を行うものである。
Therefore, the present invention solves the problem of making a state where it can be used as it is without requiring a molding process or the like after the soot treatment, and further only the soot treatment process, and the like, such as the mixed solution and the chemical solution. Therefore, the ant / preservative treatment is performed at a low cost without the need for this step.

本願発明の燻煙処理装置は、
木材を内部に配置出来て、密閉可能な燻煙処理室と
前記燻煙処理室外に配置され、燃料を不完全燃焼することで煙を発生する煙発生部と、
前記燻煙処理室の一側面と前記煙発生部を接続し、前記煙発生部で発生した煙を、放熱しつつ前記燻煙処理室に導く第1の配管と、
前記燻煙処理室の上面に接続され、前記燻煙処理室の内部の空気を排出する第2の配管と、
前記燻煙処理室の内側面の上部に配置され、前記燻煙処理室の内部の空気を対向する側面に向けて移動させるファンと、
前記燻煙処理室の内部で前記ファンに対向する位置に傾斜して配置され、前記ファンによって移動された空気の移動方向を下方に変更することにより前記燻煙処理室の内部の煙を循環させる板材と、
を有し、
前記煙発生部の燃焼量を調整して前記燻煙処理室内の温度を50℃以下として燻煙処理室内に配置した木材を燻煙処理する
ことを特徴とする木材の燻煙処理装置である。
また、本願発明の木材を燻煙処理する方法は、
木材を内部に配置した密閉された燻煙処理室に、燃料を不完全燃焼させて発生させた煙を供給して充満し、
前記燻煙処理室内の温度を50℃以下に保持しつつ、
前記燻煙処理室内の煙を循環させつつ、
前記燻煙処理室内で木材を2〜4日間燻煙する、
ものである。
The soot treatment device of the present invention is
Wood can be placed inside, a smoke treatment chamber that can be sealed ,
A smoke generator disposed outside the soot processing chamber and generating smoke by incomplete combustion of the fuel ;
Wherein the one side of smoking treatment chamber Connect the smoke generator, smoke generated by the smoke generator, a first pipe leading to the smoking treatment chamber while heat radiation,
A second pipe connected to the upper surface of the soot treatment chamber and exhausting the air inside the soot treatment chamber;
A fan that is arranged at the upper part of the inner side surface of the soot processing chamber and moves the air inside the soot processing chamber toward the opposite side surface;
The smoke is disposed at a position facing the fan inside the smoke treatment chamber, and the smoke inside the smoke treatment chamber is circulated by changing the moving direction of the air moved by the fan downward. Board material,
Have
A wood smoke treatment apparatus, wherein the wood disposed in the smoke treatment chamber is smoked by adjusting the amount of combustion in the smoke generating section so that the temperature in the smoke treatment chamber is 50 ° C. or lower.
In addition, the method of smoke treatment of the wood of the present invention,
Supplying and filling smoke generated by incomplete combustion of fuel into a sealed soot processing chamber with wood inside,
While maintaining the temperature in the smoke processing chamber at 50 ° C. or lower,
While circulating the smoke in the smoke processing chamber,
Smoke wood for 2-4 days in the smoke treatment chamber,
Is.

木材を、50℃を超える環境に配置し、その温度を持続すると木材中の水分が蒸発する。その蒸発によって木材の変形が発生することが知られており、その変形をできるだけ小さくするように様々な乾燥手法がとられている。また、木材を乾燥させる場合は、50℃を超える温度で行わないと十分な乾燥ができないか、又は過大な時間を要し現実的では無い。しかし本願発明では木材をあらかじめ乾燥させておき、発生した変形は成形加工によって修正し、所望の形状になって乾燥処理が完了した後の木材に、燻煙処理のみを施すものである。その燻煙処理においては燻煙処理室の温度を50℃以下に保つことで当該木材がさらに乾燥することを防止し、木材の変形を防止するため、燻煙処理後に追加の成形加工が不要となり、当該木材の表面に施した燻煙処理を維持したまま建築等に使用することが可能となるのである。   When wood is placed in an environment exceeding 50 ° C. and the temperature is maintained, moisture in the wood evaporates. It is known that the deformation of the wood is caused by the evaporation, and various drying methods are taken so as to make the deformation as small as possible. In addition, when drying wood, sufficient drying is not possible unless it is performed at a temperature exceeding 50 ° C., or excessive time is required, which is not practical. However, in the present invention, the wood is dried in advance, and the generated deformation is corrected by a molding process, and only the smoke treatment is performed on the wood after the desired shape is obtained and the drying treatment is completed. In the soot treatment, the temperature of the soot treatment chamber is kept at 50 ° C. or lower to prevent further drying of the wood and to prevent deformation of the wood, so that no additional molding process is required after the soot treatment. It becomes possible to use it for construction or the like while maintaining the smoke treatment applied to the surface of the wood.

本願発明の燻煙処理装置は、
前記燻煙処理室外に、前記煙発生部とは独立して配置され、空気を加熱する熱発生部と、
前記燻煙処理室の前記一側面と前記熱発生部とを接続し、前記第1の配管よりも短く、前記熱発生部で加熱された空気を前記燻煙処理室に導くことにより、前記燻煙処理とは異なってより高い温度設定にして、前記燻煙処理室で木材の乾燥可能とする第3の配管と、
前記燻煙処理室の前記一側面に対向する一側面に配置された開閉扉と、
をさらに備えてもよい。
また、本願発明の木材を乾燥処理及び燻煙処理する方法は、前記燻煙処理室に、加熱した空気を供給して、前記燻煙処理室内の温度を60℃〜80℃に保持しつつ、前記燻煙処理室内で木材を8〜10日間乾燥し、乾燥した木材を前記燻煙処理室から取り出して表面加工し、表面加工した木材を前記燻煙処理室に配置し、木材を燻煙処理する方法を実行するものである。
The soot treatment device of the present invention is
Outside the smoking treatment chamber, wherein the smoke generator is disposed independently, a heat generator for heating the air,
The one side surface of the soot processing chamber is connected to the heat generating unit, and the air heated by the heat generating unit, which is shorter than the first pipe, is guided to the soot processing chamber. the smoke treated in the higher temperature setting than I different, a third pipe for allowing the drying of wood in the smoking treatment chamber,
An open / close door disposed on one side surface of the smoke processing chamber facing the one side surface;
May be further provided.
In addition, the method of drying and smoke treatment of the wood of the present invention supplies heated air to the smoke treatment chamber and maintains the temperature in the smoke treatment chamber at 60 ° C. to 80 ° C., Wood is dried in the soot treatment chamber for 8 to 10 days, the dried wood is taken out from the soot treatment chamber and surface-treated, the surface-treated wood is placed in the soot treatment chamber, and the wood is treated with smoke To execute the method.

本願発明の燻煙処理装置は、前記煙発生部とは異なる熱発生部を備え、当該熱発生部で発生した熱を前記燻煙処理室に送り、前記燻煙処理を行うときとは異なる温度に設定することで、前記燻煙処理室を木材の乾燥に使用することも可能である。これによって別途木材の乾燥を行う装置等を用意することが無く設置場所や装置コストの減少につながる。   The smoke treatment apparatus of the present invention includes a heat generation unit different from the smoke generation unit, sends heat generated in the heat generation unit to the smoke treatment chamber, and a temperature different from that when performing the smoke treatment. It is also possible to use the smoke processing chamber for drying wood. As a result, there is no need to prepare a separate device for drying wood, which leads to a reduction in installation location and cost.

本願発明によれば、乾燥した後に成形加工を終わらせた木材に燻煙処理を行うことで、燻煙処理後に成形加工を行うことで燻煙処理の効果を失うことも無く、別途薬品などを用いることも無く十分な防腐・防蟻効果を発揮することが可能となる。   According to the present invention, by performing smoke treatment on the wood that has been molded after drying, the effect of the smoke treatment is not lost by performing the molding process after the smoke treatment. It is possible to exhibit a sufficient antiseptic and ant-proof effect without using it.

本願発明の燻煙処理装置の全体外観を示した斜視図である。It is the perspective view which showed the whole external appearance of the soot processing apparatus of this invention. 同装置の扉を開けた状態の側面図である。It is a side view of the state which opened the door of the apparatus. 同装置の木材搬入状態を示した斜視図である。It is the perspective view which showed the timber carrying state of the same apparatus. 同装置の正面図である。It is a front view of the same apparatus. 本装置で処理した木材の試験結果を表す写真である。It is a photograph showing the test result of the wood processed with this device.

(実施例1)
以下、本願発明を実施する形態を、実施例として図面を参照しながら説明する。図1は、本願発明に係る燻煙処理装置の実施例の全体外観の斜視図である。燻煙処理室10は密閉可能な構造であり、本実施例においてはコンテナを改造して用いている。燻煙処理室10は、室外の温度の影響を受けにくくするために内部に断熱材を配置するのが好ましい。燻煙処理室10の1面には大きく開口する扉11が備えられており、前記扉11を開き燻煙処理する木材100を搬入・搬出する。木材100の搬入・搬出は、台車12を使用して行う。台車12は木材を載せる枠13と下部に配置した車輪14からなっており、当該車輪は燻煙処理室床面から外部に通じるレール(図示せず)上を移動可能な構成となっている。
Example 1
Hereinafter, embodiments of the present invention will be described as examples with reference to the drawings. FIG. 1 is a perspective view of the overall appearance of an embodiment of a soot processing apparatus according to the present invention. The smoke processing chamber 10 has a sealable structure, and in this embodiment, a container is modified. The smoke processing chamber 10 is preferably provided with a heat insulating material in order to make it less susceptible to the influence of outdoor temperature. A door 11 having a large opening is provided on one surface of the smoke treatment chamber 10, and the door 11 is opened to carry in and out the wood 100 to be smoke treated. Carrying in / out of the wood 100 is performed using a carriage 12. The carriage 12 includes a frame 13 on which wood is placed and a wheel 14 disposed at the lower part, and the wheel is configured to be movable on a rail (not shown) that communicates with the outside from the floor surface of the smoke treatment chamber.

手順としては、燻煙処理室10の扉11を開き、台車12を燻煙処理室10の外へ引き出す。当該台車12の枠14の上に燻煙処理を行う木材100を配置する。このとき、木材どうしの間に煙が十分通るように必要な隙間を空けておく。図示したような大きさの木材であれば手作業でも配置することは可能であるが、大きな木材であれば、台車12は外に露出している状態なのでフォークリフトを用いて木材を配置することも可能である。   As a procedure, the door 11 of the smoke processing chamber 10 is opened, and the cart 12 is pulled out of the smoke processing chamber 10. On the frame 14 of the cart 12, the wood 100 that performs the smoke treatment is disposed. At this time, leave a necessary gap so that smoke passes between the woods. If the wood is as shown in the figure, it can be placed manually, but if it is a large wood, the cart 12 is exposed to the outside so that the wood can be placed using a forklift. Is possible.

次に、木材100を配置した台車12を燻煙処理室10へ戻し、扉11を閉め、燻煙処理室10を密閉状態にする。その後煙発生部20から燻煙処理室10へ煙を送る。   Next, the carriage 12 on which the wood 100 is disposed is returned to the soot processing chamber 10, the door 11 is closed, and the soot processing chamber 10 is sealed. Thereafter, smoke is sent from the smoke generation unit 20 to the soot processing chamber 10.

煙発生部20は、本実施例では製材所等で発生する木屑・かんな屑を燃焼させて発生させる。大量の木屑・かんな屑を煙発生部20に投入し着火するのだが、燃焼に必要な空気量を少なくし、不完全燃焼状態とすることで大量の煙が発生する。その煙は配管21内を移動し、燻煙処理室10へ移動する。煙発生部20で発生した燃焼熱は、配管21が十分な長さをもっているため大気中に放出されて、燻煙処理室へ伝わることが無く、燻煙処理室の温度上昇を抑えることが可能である。念のため燻煙処理室10内に接地した温度計(図示せず)により燻煙処理室10内の温度を確認するが、発明者が何度も実証試験を行っても50℃を超えることは無かった。しかし温度が上昇しすぎることがあれば、煙発生部20の燃焼量を調整することで温度調整が可能である。   In the present embodiment, the smoke generation unit 20 generates wood waste and kana waste generated at a sawmill or the like by burning. A large amount of wood and plank waste is put into the smoke generator 20 and ignited, but a large amount of smoke is generated by reducing the amount of air required for combustion and incomplete combustion. The smoke moves in the pipe 21 and moves to the smoke processing chamber 10. The combustion heat generated in the smoke generation unit 20 is released into the atmosphere because the pipe 21 has a sufficient length, and is not transmitted to the smoke treatment chamber, so that the temperature rise in the smoke treatment chamber can be suppressed. It is. As a precaution, the temperature inside the soot processing chamber 10 is confirmed by a thermometer (not shown) grounded in the soot processing chamber 10, but the temperature exceeds 50 ° C. even if the inventor has conducted many verification tests. There was no. However, if the temperature rises too much, the temperature can be adjusted by adjusting the amount of combustion of the smoke generating unit 20.

本実施例においては、後述する実施例2によって乾燥処理を済ませた杉材の燻煙処理を行った。また、本願発明の燻煙処理装置以外の方法によって乾燥処理が完了した木材を用いても良い。所定の寸法に加工された木材100を燻煙処理室に配置し、煙発生部20からの煙を燻煙処理室10に充満させて2〜4日間燻煙処理を行う。木材100のそれぞれに均一に煙があたるように電動ファン50によって攪拌を行う。電動ファンはそれぞれモーター51によって回転し、処理室の煙が充満した空気を一方向へ動かすものであるが、燻煙処理室10内部の上方に配置した板15によって下方向へ移動し、さらに燻煙処理室10内部の下方に配置した板16によって横方向へ移動する。これらの電動ファン50、上方に配置した板15及び下方に配置した板16によって煙は燻煙処理室10内を循環しながら一定の煙濃度となることとで、燻煙処理のムラが発生することを防止する。   In this example, the smoke treatment of the cedar wood that had been dried according to Example 2 described later was performed. Moreover, you may use the wood which the drying process completed by methods other than the soot processing apparatus of this invention. The wood 100 processed into a predetermined size is placed in the soot processing chamber, the smoke from the smoke generating unit 20 is filled in the soot processing chamber 10, and the soot processing is performed for 2 to 4 days. Stirring is performed by the electric fan 50 so that smoke is uniformly applied to each of the woods 100. Each of the electric fans is rotated by a motor 51 to move the air filled with smoke in the processing chamber in one direction. However, the electric fan is moved downward by a plate 15 disposed above the inside of the smoke processing chamber 10, and further It moves laterally by a plate 16 disposed below the inside of the smoke treatment chamber 10. By the electric fan 50, the plate 15 disposed above and the plate 16 disposed below, the smoke becomes a constant smoke concentration while circulating in the smoke treatment chamber 10, thereby causing unevenness in the smoke treatment. To prevent that.

燻煙処理室10内に煙を送り込み続けると、やがて煙があふれ出してしまう。そこで上部に配置した配管22から余った煙を放出する。配管22の途中にはブロワー61を配置し、煙を強制的に排出することも可能であるし、自然排出させても良い。上部に配置した配管22の先端は、燻煙処理室10上に配置した排煙槽60内に配置する。排煙層60には水をためておき、排煙が水を通過することで水に吸収されるので、屋外に排煙が排出することは無く、環境に配慮した構成としている。   If smoke continues to be sent into the smoke processing chamber 10, the smoke will eventually overflow. Therefore, excess smoke is discharged from the pipe 22 arranged in the upper part. A blower 61 is disposed in the middle of the pipe 22 so that smoke can be forcibly discharged or may be discharged naturally. The tip of the pipe 22 arranged at the upper part is arranged in the smoke exhausting tank 60 arranged on the smoke processing chamber 10. Water is stored in the flue gas layer 60, and the flue gas is absorbed by the water as it passes through the water. Therefore, the flue gas is not discharged outdoors, and is configured in consideration of the environment.

この燻煙処理が完了した木材は適度の着色がなされ外観品質の向上がはかられ、当該木材の表面のみならず、内部にまで防腐・防蟻効果がなされている。以下に防蟻効果の実証試験を説明する。   The wood that has been subjected to the smoke treatment is appropriately colored to improve the appearance quality, so that not only the surface of the wood but also the inside is preserved and preserved. The verification test of the ant-proof effect is described below.

(実証試験)
本装置での燻煙処理の防虫効果試験結果を以下に記す。本試験は京都大学生存圏研究所居住権環境共生分野に依頼した試験である。目的は試験体の耐シロアリ性能を室内試験によって検証するものである。試験材料は発明者が平成25年10月に富山県氷見市岩瀬の山林から伐採した樹齢約40年の杉である。試験体のサイズは、20×20×10mmである。試験体は3種類で、Aは燻煙処理を行わないもの。Bは本装置で2日間燻煙処理をしたもの。Cは本装置で4日間燻煙処理をしたものであり、大学側が用意した対照材とともに行った。
(Verification test)
The results of the insect repellent effect test of smoke treatment with this device are shown below. This test was commissioned to the living environment symbiosis field of the Kyoto University Institute for Life Sphere. The purpose is to verify the termite resistance of the specimen by laboratory tests. The test material is about 40 years old cedar cut by the inventor from Iwase Forest in Himi City, Toyama Prefecture in October 2013. The size of the test body is 20 × 20 × 10 mm. There are three types of test specimens, and A is a sample that does not perform smoke treatment. B is smoked with this device for 2 days. C was smoked with this device for 4 days and was used together with a control material prepared by the university.

試験方法として、耐シロアリ試験は、京都大学生存圏研究所居住圏環境共生分野で室内飼育中のイエシロアリを用い、JIS K 1571-2010「木材保存剤―性能基準及びその試験方法」に準じて行った。底部を硬石膏で固めたアクリル製円筒容器(内径80mm、高さ60mm)の 中央部にプラスチック製メッシュを置き、その上に耐候操作(本願発明の燻煙処理)を施した試験体1個をセットした。室内飼育コロニーよりイエシロ アリを採取し、職蟻150頭、兵蟻15頭を同容器内に投入した。これを湿らせた脱脂綿を敷き詰めた容器内に入れ、28℃、暗所で保管した。   As a test method, the termite resistance test was conducted according to JIS K 1571-2010 “Wood preservatives-Performance criteria and test methods” using the termites that are housed indoors in the living environment symbiosis field of the Institute for Living Areas of Kyoto University. It was. Place a plastic mesh in the center of an acrylic cylindrical container (inner diameter: 80mm, height: 60mm) that has been hardened with anhydrite on the bottom. I set it. Termite ants were collected from an indoor breeding colony and 150 craft ants and 15 soldier ants were put into the container. This was placed in a container spread with moistened absorbent cotton and stored at 28 ° C. in the dark.

3週間後試験体を取り出し、試験前後の試験体の質量変化から質量減少を算出した(図5参照)。また、同時に供試虫の死亡率についても測定を行った。試験個数は5個である。表1に試験結果をまとめて示す。   After 3 weeks, the specimen was taken out, and the mass decrease was calculated from the mass change of the specimen before and after the test (see FIG. 5). At the same time, the mortality of the test insects was also measured. The number of tests is five. Table 1 summarizes the test results.

(試験結果)
対照材として用いたスギ辺材の平均質量減少量および平均質量減少率は、それぞれ242.0mg及び18.1%であった。JIS規格の定める試験の成立基準は平均質量減少率15%以上というものであり、本試験で用いたシロアリの活性には問題はなかったと判断される。試験体Aはスギ辺材とほぼ同程度の激しい食害を受け、耐シロアリ性は全く有していなかった。一方、試験体B、Cの平均質量減少量及び平均質量減少率は、それぞれ 68.8mgと49.8mg、及び5.0%と3.5%であり、試験体Aと比較して耐シロアリ性は著しく上昇した。特に試験体Cでは、質量減少率3%以下というJIS規格における木材保存剤としての性能基準に近いレベルまで食害は低下した。3週間後の職蟻の死亡率が試験体B及びCにおいても50%未満であることから、これらの試験体における耐シロアリ性の向上は、殺シロアリ性に由来するものではなく、忌避作用によるものであると推察することができる、という試験結果を得た。
(Test results)
The average mass loss and the average mass reduction rate of the cedar sapwood used as the control material were 242.0 mg and 18.1%, respectively. The standard for establishing the test defined by the JIS standard is an average mass reduction rate of 15% or more, and it is judged that there was no problem with the activity of the termites used in this test. Specimen A suffered severe damage from cedar sapwood and had no termite resistance at all. On the other hand, the average mass loss and the average mass reduction rate of specimens B and C were 68.8 mg and 49.8 mg, and 5.0% and 3.5%, respectively, and the termite resistance was remarkably increased as compared with specimen A. In particular, in the test body C, the food damage decreased to a level close to the performance standard as a wood preservative in the JIS standard of 3% or less in mass reduction rate. Since the mortality rate of ants after 3 weeks is less than 50% in specimens B and C, the improvement in termite resistance in these specimens is not due to termite killing but is due to repellent action The test result that it was possible to guess that it was a thing was obtained.

(実施例2)
以下に、本願発明の燻煙処理装置を用いて、乾燥処理を行う場合を説明する。木材100を燻煙処理室10に配置する方法は実施例1と同様であり説明を省くが、木材100は乾燥処理によって収縮・変形が発生する。そのためあらかじめその収縮・変形量を見込んで、製品として必要な大きさよりも大きな材料として加工しておく。
(Example 2)
Below, the case where a drying process is performed using the smoke processing apparatus of this invention is demonstrated. The method of arranging the wood 100 in the smoke processing chamber 10 is the same as that in the first embodiment and will not be described. However, the wood 100 is shrunk and deformed by the drying process. Therefore, it is processed in advance as a material larger than the size required for the product, considering the amount of shrinkage and deformation.

乾燥処理においては、煙発生部20は使用しない。熱発生部30に木屑・かんな屑などの燃焼材料を投入し、煙発生部20で煙を発生するときとは異なり、十分な酸素が供給されるようにして完全燃焼させる。この燃焼により発生した熱は、高温の空気となって燻煙処理室10内に送られる。配管23は短くなるように配置してあり配管での熱放出も少ない。   In the drying process, the smoke generator 20 is not used. Unlike the case where smoke is generated in the smoke generation unit 20 by introducing a combustion material such as wood chips or kana scrap into the heat generation unit 30, complete combustion is performed so that sufficient oxygen is supplied. The heat generated by this combustion becomes hot air and is sent into the smoke processing chamber 10. The piping 23 is arranged so as to be short, and the heat release in the piping is also small.

燻煙処理室内に送られた熱風は、実施例1と同様に電動ファン50により循環され、すべての木材100に均等にあてられる。発明者が何度も実証試験を行った結果、燻煙処理室10の内部温度は60℃〜80℃に維持されることがわかった。この状態のまま8日〜10日保持する。これにより木材100の乾燥度を所定の値にする事が出来る。   The hot air sent into the smoke processing chamber is circulated by the electric fan 50 in the same manner as in the first embodiment, and is equally applied to all the wood 100. As a result of the inventor's repeated verification tests, it was found that the internal temperature of the smoke treatment chamber 10 was maintained at 60 ° C to 80 ° C. Hold in this state for 8-10 days. Thereby, the dryness of the wood 100 can be set to a predetermined value.

乾燥が完了した木材100は、燻煙処理室10から一旦出され、乾燥による収縮・変形を矯正するために、再度表面加工を行う。当該加工が完了した木材を燻煙加工するために、実施例1の内容で燻煙処理を行う。   The wood 100 that has been dried is once removed from the smoke processing chamber 10 and subjected to surface processing again in order to correct shrinkage and deformation due to drying. In order to smoke-process the finished wood, the smoke treatment is performed according to the contents of Example 1.

10 燻煙処理室、
11 扉、
12 台車、
13 枠、
14 車輪、
15、16 整流板、
20 煙発生部、
21、22、23 配管、
30 熱発生部、
50 電動ファン、
60 排煙処理槽、
61 ブロワー、
100 木材
10 Smoke treatment room,
11 Door,
12 carts,
13 frames,
14 wheels,
15, 16 current plate,
20 Smoke generator,
21, 22, 23 piping,
30 heat generating part,
50 electric fan,
60 Smoke treatment tank,
61 Blower,
100 wood

Claims (4)

木材を内部に配置出来て、密閉可能な燻煙処理室と
前記燻煙処理室外に配置され、燃料を不完全燃焼することで煙を発生する煙発生部と、
前記燻煙処理室の一側面と前記煙発生部を接続し、前記煙発生部で発生した煙を、放熱しつつ前記燻煙処理室に導く第1の配管と、
前記燻煙処理室の上面に接続され、前記燻煙処理室の内部の空気を排出する第2の配管と、
前記燻煙処理室の内側面の上部に配置され、前記燻煙処理室の内部の空気を対向する側面に向けて移動させるファンと、
前記燻煙処理室の内部で前記ファンに対向する位置に傾斜して配置され、前記ファンによって移動された空気の移動方向を下方に変更することにより前記燻煙処理室の内部の煙を循環させる板材と、
を有し、
前記煙発生部の燃焼量を調整して前記燻煙処理内の温度を50℃以下として燻煙処理室内に配置した木材を燻煙処理する
ことを特徴とする木材の燻煙処理装置。
Wood can be placed inside, a smoke treatment chamber that can be sealed ,
A smoke generator disposed outside the soot processing chamber and generating smoke by incomplete combustion of the fuel ;
Wherein the one side of smoking treatment chamber Connect the smoke generator, smoke generated by the smoke generator, a first pipe leading to the smoking treatment chamber while heat radiation,
A second pipe connected to the upper surface of the soot treatment chamber and exhausting the air inside the soot treatment chamber;
A fan that is arranged at the upper part of the inner side surface of the soot processing chamber and moves the air inside the soot processing chamber toward the opposite side surface;
The smoke is disposed at a position facing the fan inside the smoke treatment chamber, and the smoke inside the smoke treatment chamber is circulated by changing the moving direction of the air moved by the fan downward. Board material,
Have
Smoking treatment apparatus of the wood, which comprises smoking treatment the smoking process was placed in a room wood the temperature in the smoking treatment chamber by adjusting the combustion amount of the smoke generator as 50 ° C. or less.
前記燻煙処理室外に、前記煙発生部とは独立して配置され、空気を加熱する熱発生部と、
前記燻煙処理室の前記一側面と前記熱発生部とを接続し、前記第1の配管よりも短く、前記熱発生部で加熱された空気を前記燻煙処理室に導くことにより、前記燻煙処理とは異なってより高い温度設定にして、前記燻煙処理室で木材の乾燥可能とする第3の配管と、
前記燻煙処理室の前記一側面に対向する一側面に配置された開閉扉と、
をさらに備える、請求項1記載の燻煙処理装置。
Outside the smoking treatment chamber, wherein the smoke generator is disposed independently, a heat generator for heating the air,
The one side surface of the soot processing chamber is connected to the heat generating unit, and the air heated by the heat generating unit, which is shorter than the first pipe, is guided to the soot processing chamber. the smoke treated with a higher temperature setting is different, a third pipe for allowing the drying of wood in the smoking treatment chamber,
An open / close door disposed on one side surface of the smoke processing chamber facing the one side surface;
The smoke processing apparatus according to claim 1 , further comprising:
木材を内部に配置した密閉された燻煙処理室に、燃料を不完全燃焼させて発生させた煙を供給して充満し、Supplying and filling smoke generated by incomplete combustion of fuel into a sealed soot processing chamber with wood inside,
前記燻煙処理室内の温度を50℃以下に保持しつつ、While maintaining the temperature in the smoke processing chamber at 50 ° C. or lower,
前記燻煙処理室内の煙を循環させつつ、While circulating the smoke in the smoke processing chamber,
前記燻煙処理室内で木材を2〜4日間燻煙する、Smoke wood for 2-4 days in the smoke treatment chamber,
木材を燻煙処理する方法。How to smoke wood.
前記燻煙処理室に、加熱した空気を供給して、Supply heated air to the smoke processing chamber,
前記燻煙処理室内の温度を60℃〜80℃に保持しつつ、前記燻煙処理室内で木材を8〜10日間乾燥し、While maintaining the temperature in the smoke treatment chamber at 60 ° C. to 80 ° C., the wood is dried in the smoke treatment chamber for 8 to 10 days,
乾燥した木材を前記燻煙処理室から取り出して表面加工し、Remove the dried wood from the smoke processing chamber and surface-treat it,
表面加工した木材を前記燻煙処理室に配置し、Place the surface-treated wood in the smoke processing chamber,
請求項3に記載の木材を燻煙処理する方法を実行する、A method for smoke treatment of wood according to claim 3 is performed.
木材を乾燥処理及び燻煙処理する方法。A method for drying and smoke treatment of wood.
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