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JP4005932B2 - Pyrolysis treatment method of waste wood - Google Patents
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JP4005932B2 - Pyrolysis treatment method of waste wood - Google Patents

Pyrolysis treatment method of waste wood Download PDF

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Publication number
JP4005932B2
JP4005932B2 JP2003066029A JP2003066029A JP4005932B2 JP 4005932 B2 JP4005932 B2 JP 4005932B2 JP 2003066029 A JP2003066029 A JP 2003066029A JP 2003066029 A JP2003066029 A JP 2003066029A JP 4005932 B2 JP4005932 B2 JP 4005932B2
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Prior art keywords
waste
wood
thermal decomposition
arsenic
cca
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JP2004267988A (en
Inventor
一雄 大貫
忠司 真鍋
安幸 中尾
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Nippon Steel Corp
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Nippon Steel Corp
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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
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W30/00Technologies for solid waste management
    • Y02W30/50Reuse, recycling or recovery technologies
    • Y02W30/58Construction or demolition [C&D] waste
    • 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
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W30/00Technologies for solid waste management
    • Y02W30/50Reuse, recycling or recovery technologies
    • Y02W30/78Recycling of wood or furniture waste

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  • Fire-Extinguishing Compositions (AREA)
  • Treating Waste Gases (AREA)
  • Processing Of Solid Wastes (AREA)
  • Coke Industry (AREA)

Description

【0001】
【発明が属する技術分野】
本発明は、建設廃棄物中に含まれる廃木材の熱分解処理方法に関し、特に、有害な砒素(As)を含有する木材系廃棄物に環境負荷のない熱分解処理を行って再資源化する熱分解処理方法に関する。
【0002】
【従来の技術】
近年、建設廃棄物は産業廃棄物全体の約2割、最終処分量の約4割を占め、さらには、産業廃棄物の不法投棄の9割を建設廃棄物が占めている。
一方、最終処分場残余年数は3年を下回り、逼迫してきている。
さらに、昭和40年代以降に急増した建築物の更新期を迎えて、今後、解体処理量が急増することが予想されている。
このように増加の一途をたどる建設廃棄物をリサイクルすることが地球環境問題における重要な課題となっている。
しかし、従来は、特に木材系廃棄物の内、防腐・防蟻のため木材にCCA(クロム(Cr)、銅(Cu)及び砒素(As)化合物系木材防腐剤をいう)を注入したCCA木材系廃棄物については、一般的な焼却を行うと有害な砒素系ガスが発生するため、埋め立て処理がなされており、資源としての再利用は十分になされていなかった。
【0003】
また、多量の建設廃棄物から選別された素材毎に適正にかつ多量に消費するシステムの構築もなされていなかった。
建設廃棄物の選別方法に関しては、例えば、特開平7−290000号公報に、土砂および可燃物を含む建設廃棄物に散水して大きな可燃物を選別した後、残りの廃棄物を乾燥してから選別工程に付することにより土砂と小さな可燃物を選別する方法が開示されている。
しかし、この技術は、建設廃棄物の選別方法を提案しているだけであり、具体的な資源としての再利用方法およびその用途に応じた処理方法は検討されていなかった。
また、特開2002−20771号公報には、廃木材の粉砕粒度を調整することによって、燃焼性および気送性を高めて高炉に装入して処理する方法が開示されている。
しかし、この技術は、廃木材を高炉に装入する際の燃焼性および気送性を高めるための条件を開示したものであって、クロム、銅、砒素という環境負荷物質の具体的な処理方法について何ら検討されていなかった。
【0004】
【特許文献1】
特開平7−290000号公報
【特許文献2】
特開2002−20771号公報
【0005】
【発明が解決しようとする課題】
本発明は、前述のような従来技術の問題点を解決し、Cr,CuおよびAsが注入されたCCA木材系廃棄物を適正に処理して、有害な砒素(As)を含有する木材系廃棄物に環境負荷のない熱分解処理を行って再資源化する熱分解処理方法を提供することを課題とする。
【0006】
【課題を解決するための手段】
発明者らは、前記の課題を解決するために鋭意検討を重ねた結果、Cr,CuおよびAsが注入されたCCA木材系廃棄物とともに硫黄含有物質を供給して熱分解処理を行うことにより、有害な砒素(As)を含有する木材系廃棄物に環境負荷のない熱分解処理を行って再資源化する熱分解処理方法を提供するものであり、その要旨とするところは、特許請求の範囲に記載した通りの下記内容である。
(1)建設廃棄物に含まれる廃木材を熱分解処理する方法において、Cr,CuおよびAsが注入されたCCA木材系廃棄物とともに、硫黄含有物質を供給して熱分解することを特徴とする廃木材の熱分解処理方法。
(2)さらに、鉄および/または銅を含有する物質を供給して熱分解することを特徴とする(1)に記載の廃木材の熱分解処理方法。
(3)前記熱分解の処理温度が500〜760℃であることを特徴とする(1)または(2)に記載の廃木材の熱分解処理方法。
(4)前記熱分解後の残さを銅精錬の副原料として使用することを特徴とする(1)乃至(3)に記載の廃木材の熱分解処理方法。
【0007】
【発明の実施の形態】
本発明の実施の形態を、図1を用いて詳細に説明する。
図1は、本発明における廃木材の熱分解処理方法を示すフロー図である。
本発明においては、Cr,CuおよびAsが注入されたCCA木材系廃棄物とともに、硫黄含有物質を供給して熱分解する。
ここに、建設廃棄物とは、ビルや家屋などの建設・解体現場から発生する木材系廃棄物を含む産業廃棄物、街路樹などの剪定時に発生する廃棄物(剪定材)等をいい、また、CCA木材系廃棄物とは、防腐・防蟻のため木材にCCA(クロム(Cr)、銅(Cu)及び砒素(As)化合物系木材防腐剤をいう)を合計0.1質量%程度注入した木材系廃棄物をいう。
本発明では、CCA木材系廃棄物とともに供給する硫黄含有物質の種類は問わないが、入手し易さという観点から、廃棄物として発生するゴムやタイヤ等が好ましい。
【0008】
硫黄(S)は砒素(As)と結びついて固定化し、熱分解の際に発生するガスや油に移行させない性質を有しているため、硫黄含有物質を供給して熱分解することにより、砒素(As)が混入しないクリーンなガスや油を提供することができる。
また、硫黄含有物質に加えて、さらに、鉄および/または銅を含有する物質を供給して熱分解することが好ましい。
鉄(Fe)には、硫黄(S)と同様に、砒素(As)を固定化する性質があり、また、銅(Cu)は砒素(As)と結合して熱力学的に安定な元素であるうえ、熱分解した残さを銅精錬工程の副原料として利用する際に、銅(Cu)の含有率が高い方が好ましいからである。
【0009】
鉄を含有する物質として、例えば、タイヤにはスチールコードとしての鉄(Fe)とゴム中の硫黄(S)の双方が含まれているため、好ましい。
また、製鉄工程で発生する製鋼ダストには多量の鉄粉が含まれているのでこれを利用してもよい。
銅を含有する物質としては、入手の容易性という観点から、建設廃棄物や廃自動車などに含まれる銅線を利用することが好ましい。
また、前記の熱分解の処理温度は500〜760℃が好ましい。
500℃未満では、廃棄物中の揮発成分が十分蒸発しないためガスや油の発生比率が低くなるうえ、760℃超では、例えば、鋼製の外熱式ロータリーキルン等の加熱設備の耐用温度を超えてしまうからである。
本発明の廃木材の熱分解処理方法によって発生した砒素(As)を実質的に含まないクリーンなガスや油は改質された後、製鉄所の発電所等の製鉄プロセスや廃棄物の処理に必要な燃料として使用できる。
【0010】
また、熱分解した残さには、Cr,Cu,Asが含まれているので、銅精錬の副原料として利用することが好ましい。
もともと銅鉱石中には微量の砒素(As)が含まれているため、銅精錬の過 程で砒素(As)の除去を行うため、副原料中に含まれる砒素(As)を銅鉱石中に含まれていた砒素と一緒にまとめて分離処理することができるからである。また、本発明によれば、Cr,Cu,Asが含まれているCCA木材系廃棄物をそのまま銅精錬工程に利用する場合に比べて、Cuの純度が高く、減容化された副原料として使用できるので、取扱いが容易であるうえ、物流コストが低減できる。
【0011】
【実施例】
内径800mm長さ6000mmの外熱式ロータリーキルンを用いて、下記条件にて、カットタイヤおよび製鋼ダストを供給してCCA木材系廃棄物の熱分解実験を行った。
<実施例−1>
熱分解温度 600℃
熱分解時間 30min
原料配合 CCA含有木材 1kgあたり
カットタイヤ 0.14kg
As固定化率 90%
<実施例−2>
熱分解温度 600℃
熱分解時間 30min
原料配合 CCA含有木材 1kgあたり
カットタイヤ 0.14kg および 製鋼ダスト 0.14kg
As固定化率 98%
<実施例−3>
熱分解温度 600℃
熱分解時間 30min
原料配合 CCA含有木材 1kgあたり
カットタイヤ 2 kg
As固定化率 98%
ここでAs固定化率とは、熱分解処理対象物中のAs含有量の総和に対する、熱分解後の残さに含まれるAs含有量の割合と定義する。 この値が100に近いほど、Asがガスや油に移行せず、環境負荷の小さい処理を実現していることを意味する。
【0012】
<実験結果>
この実験の結果、カットタイヤをCCA含有木材1kgあたり0.14kg供給した実施例−1では、砒素(As)の固定化率は90%であり、また、カットタイヤ 0.14kgおよび製鉄ダスト0.14kgを供給した実施例−2と、カットタイヤ 2 kgを供給した実施例−3では、砒素(As)の固定化率は98%であった。
すなわち、熱分解により発生するガスや油には、実施例−1ではCCA含有木材中の砒素(As)の10%、実施例−2および実施例−3ではCCA含有木材中の砒素(As)の2%しか移行しなかった。
従って、本発明によれば、硫黄含有物質を供給せずに熱分解した場合の砒素(As)の固定化率約50%に比べて著しく固定化率を上昇させることができ、実質的に砒素(As)を含有しないクリーンなガスや油を提供することができることが確認された。
【0013】
【発明の効果】
本発明によれば、Cr,CuおよびAsが注入されたCCA木材系廃棄物とともに硫黄含有物質を供給して熱分解処理を行うことにより、有害な砒素(As)を含有する木材系廃棄物に環境負荷のない熱分解処理を行って再資源化する熱分解処理方法を提供することができるなど、産業上有用な著しい効果を奏する。
【図面の簡単な説明】
【図1】 本発明における廃木材の熱分解処理方法を示すフロー図である。
[0001]
[Technical field to which the invention belongs]
TECHNICAL FIELD The present invention relates to a method for thermally decomposing waste wood contained in construction waste, and in particular, recycles wood waste containing harmful arsenic (As) by carrying out pyrolysis without environmental impact. The present invention relates to a thermal decomposition method.
[0002]
[Prior art]
In recent years, construction waste accounts for about 20% of the total industrial waste and about 40% of the final disposal amount. Furthermore, construction waste accounts for 90% of illegal dumping of industrial waste.
On the other hand, the remaining years of the final disposal site are less than 3 years and are becoming tight.
Furthermore, with the renewal period of buildings rapidly increasing since the Showa 40s, it is expected that the amount of dismantling will increase rapidly in the future.
Recycling construction waste, which continues to increase, is an important issue in global environmental problems.
However, in the past, CCA wood in which CCA (referred to as chromium (Cr), copper (Cu) and arsenic (As) compound wood preservatives) was injected into wood for preserving and preventing ants, especially among wood wastes. As for system wastes, harmful arsenic gases are generated when incinerated, and therefore, landfill treatment has been performed, and reuse as resources has not been made sufficiently.
[0003]
In addition, a system that appropriately consumes a large amount for each material selected from a large amount of construction waste has not been constructed.
Concerning the sorting method of construction waste, for example, in Japanese Patent Application Laid-Open No. 7-290000, after spraying the construction waste containing earth and sand and combustible material to sort out large combustible material, the remaining waste material is dried. A method for sorting earth and sand and small combustibles by subjecting them to a sorting step is disclosed.
However, this technology only proposes a method for sorting construction waste, and a reuse method as a specific resource and a treatment method according to its use have not been studied.
Japanese Patent Application Laid-Open No. 2002-20771 discloses a method in which the pulverized particle size of waste wood is adjusted to increase the combustibility and air transportability and to be charged into a blast furnace.
However, this technology discloses conditions for enhancing combustibility and air transportability when waste wood is charged into a blast furnace, and is a specific method for treating environmentally hazardous substances such as chromium, copper, and arsenic. There was nothing to be considered about.
[0004]
[Patent Document 1]
JP-A-7-290000 [Patent Document 2]
Japanese Patent Laid-Open No. 2002-20771
[Problems to be solved by the invention]
The present invention solves the problems of the prior art as described above, and appropriately treats CCA wood wastes injected with Cr, Cu and As to produce wood wastes containing harmful arsenic (As). It is an object of the present invention to provide a thermal decomposition processing method for recycling resources by performing thermal decomposition processing without environmental impact.
[0006]
[Means for Solving the Problems]
As a result of intensive studies in order to solve the above-mentioned problems, the inventors have conducted a thermal decomposition treatment by supplying a sulfur-containing material together with a CCA wood-based waste material into which Cr, Cu and As have been injected, The present invention provides a thermal decomposition method for recycling a waste material containing harmful arsenic (As) by carrying out thermal decomposition treatment without environmental impact, and the gist of the invention is as follows. It is the following contents as described in.
(1) In the method of thermally decomposing waste wood contained in construction waste, a sulfur-containing material is supplied and pyrolyzed together with CCA wood waste injected with Cr, Cu and As. Thermal decomposition method for waste wood.
(2) The method for thermally decomposing waste wood according to (1), further comprising supplying a substance containing iron and / or copper to thermally decompose.
(3) The thermal decomposition treatment method of waste wood according to (1) or (2), wherein the thermal decomposition treatment temperature is 500 to 760 ° C.
(4) The method for pyrolyzing waste wood according to any one of (1) to (3), wherein the residue after pyrolysis is used as an auxiliary material for copper refining.
[0007]
DETAILED DESCRIPTION OF THE INVENTION
An embodiment of the present invention will be described in detail with reference to FIG.
FIG. 1 is a flowchart showing a method for thermally decomposing waste wood according to the present invention.
In the present invention, a sulfur-containing material is supplied and pyrolyzed together with CCA wood-based waste injected with Cr, Cu and As.
Here, construction waste refers to industrial waste including wood-based waste generated from construction and demolition sites such as buildings and houses, waste generated when pruning roadside trees (pruning material), etc. , CCA wood waste is about 0.1% by mass of CCA (chromium (Cr), copper (Cu) and arsenic (As) compound wood preservatives) in total for preserving and preventing ants. Wood waste.
In the present invention, the type of sulfur-containing material supplied together with the CCA wood-based waste is not limited, but rubber, tires, and the like generated as waste are preferable from the viewpoint of easy availability.
[0008]
Sulfur (S) is fixed in combination with arsenic (As) and has the property of not being transferred to gas or oil generated during thermal decomposition. It is possible to provide clean gas or oil that does not contain (As).
In addition to the sulfur-containing material, it is preferable to further thermally decompose by supplying a material containing iron and / or copper.
Iron (Fe), like sulfur (S), has the property of immobilizing arsenic (As), and copper (Cu) is a thermodynamically stable element that combines with arsenic (As). In addition, when the pyrolyzed residue is used as an auxiliary material in the copper refining process, a higher copper (Cu) content is preferable.
[0009]
As a substance containing iron, for example, a tire contains both iron (Fe) as a steel cord and sulfur (S) in rubber, which is preferable.
Moreover, since a large amount of iron powder is contained in the steelmaking dust generated in the iron making process, it may be used.
As a substance containing copper, it is preferable to use a copper wire contained in construction waste or a scrapped vehicle from the viewpoint of easy availability.
The thermal decomposition treatment temperature is preferably 500 to 760 ° C.
If it is less than 500 ° C, the generation ratio of gas and oil is low because the volatile components in the waste are not sufficiently evaporated, and if it exceeds 760 ° C, it exceeds the service temperature of heating equipment such as a steel external heating rotary kiln. Because it will end up.
The clean gas and oil substantially free of arsenic (As) generated by the thermal decomposition treatment method of waste wood according to the present invention is reformed and then used for iron making processes such as power plants in steelworks and waste disposal. It can be used as a necessary fuel.
[0010]
Further, since the pyrolyzed residue contains Cr, Cu, As, it is preferably used as an auxiliary material for copper refining.
Since copper ore originally contains trace amounts of arsenic (As), arsenic (As) contained in the auxiliary raw materials is contained in the copper ore in order to remove arsenic (As) during the copper refining process. This is because they can be separated together with the contained arsenic. In addition, according to the present invention, the CCA wood-based waste containing Cr, Cu, As is used as it is in the copper refining process as it is, and the purity of Cu is high and as a reduced raw material. Since it can be used, it is easy to handle and logistics costs can be reduced.
[0011]
【Example】
Using an externally heated rotary kiln with an inner diameter of 800 mm and a length of 6000 mm, cut tires and steelmaking dust were supplied under the following conditions to conduct thermal decomposition experiments on CCA wood waste.
<Example-1>
Thermal decomposition temperature 600 ℃
Pyrolysis time 30min
Material mix CCA-containing wood 1kg of cut tires per 1kg
As immobilization rate 90%
<Example-2>
Thermal decomposition temperature 600 ℃
Pyrolysis time 30min
Raw material mix CCA containing wood 0.14kg of cut tires per 1kg and 0.14kg of steelmaking dust
As immobilization rate 98%
<Example-3>
Thermal decomposition temperature 600 ℃
Pyrolysis time 30min
Material mix CCA-containing wood 1 kg of cut tires per 1 kg
As immobilization rate 98%
Here, the As immobilization rate is defined as the ratio of the As content contained in the residue after pyrolysis to the total As content in the thermal decomposition treatment object. As this value is closer to 100, As does not shift to gas or oil, which means that processing with a small environmental load is realized.
[0012]
<Experimental result>
As a result of this experiment, in Example-1 in which 0.14 kg of cut tire was supplied per 1 kg of CCA-containing wood, the arsenic (As) immobilization rate was 90%, and 0.14 kg of cut tire and 0.14 kg of steelmaking dust were supplied. In Example 2 and Example 3 in which 2 kg of cut tires were supplied, the arsenic (As) immobilization rate was 98%.
That is, in the gas and oil generated by thermal decomposition, 10% of arsenic (As) in the CCA-containing wood is used in Example 1, and arsenic (As) in the CCA-containing wood is used in Examples 2 and 3. Only 2%.
Therefore, according to the present invention, the immobilization rate can be remarkably increased as compared with the immobilization rate of about 50% of arsenic (As) when pyrolyzing without supplying a sulfur-containing substance. It was confirmed that clean gas and oil not containing (As) can be provided.
[0013]
【The invention's effect】
According to the present invention, by supplying a sulfur-containing substance together with CCA wood waste into which Cr, Cu and As are injected, and performing a thermal decomposition treatment, the wood waste containing harmful arsenic (As) is obtained. An industrially useful remarkable effect can be provided, for example, by providing a thermal decomposition method for recycling by performing thermal decomposition treatment without environmental load.
[Brief description of the drawings]
BRIEF DESCRIPTION OF DRAWINGS FIG. 1 is a flowchart showing a method for thermally decomposing waste wood according to the present invention.

Claims (4)

建設廃棄物に含まれる廃木材を熱分解処理する方法において、Cr,CuおよびAsが注入されたCCA木材系廃棄物とともに、硫黄含有物質を供給して熱分解することを特徴とする廃木材の熱分解処理方法。In a method for thermally decomposing waste wood contained in construction waste, the waste wood is characterized in that it is pyrolyzed by supplying a sulfur-containing material together with CCA wood waste injected with Cr, Cu and As. Thermal decomposition method. さらに、鉄および/または銅を含有する物質を供給して熱分解することを特徴とする請求項1に記載の廃木材の熱分解処理方法。The method for pyrolyzing waste wood according to claim 1, further comprising supplying a substance containing iron and / or copper for pyrolysis. 前記熱分解の処理温度が500〜760℃であることを特徴とする請求項1または請求項2に記載の廃木材の熱分解処理方法。The thermal decomposition treatment method for waste wood according to claim 1 or 2, wherein the thermal decomposition treatment temperature is 500 to 760 ° C. 前記熱分解後の残さを銅精錬の副原料として使用することを特徴とする請求項1乃至請求項3に記載の廃木材の熱分解処理方法。The method for pyrolyzing waste wood according to any one of claims 1 to 3, wherein the residue after pyrolysis is used as an auxiliary material for copper refining.
JP2003066029A 2003-03-12 2003-03-12 Pyrolysis treatment method of waste wood Expired - Fee Related JP4005932B2 (en)

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JP3886970B2 (en) * 2004-01-13 2007-02-28 三菱重工業株式会社 Recycling method of wood
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