JP2003168370A - Mercury recovery method of waste fluorescent lamp and its device - Google Patents
Mercury recovery method of waste fluorescent lamp and its deviceInfo
- Publication number
- JP2003168370A JP2003168370A JP2001367277A JP2001367277A JP2003168370A JP 2003168370 A JP2003168370 A JP 2003168370A JP 2001367277 A JP2001367277 A JP 2001367277A JP 2001367277 A JP2001367277 A JP 2001367277A JP 2003168370 A JP2003168370 A JP 2003168370A
- Authority
- JP
- Japan
- Prior art keywords
- mercury
- hot water
- arc tube
- fluorescent lamp
- glass member
- 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.)
- Granted
Links
- QSHDDOUJBYECFT-UHFFFAOYSA-N mercury Chemical compound [Hg] QSHDDOUJBYECFT-UHFFFAOYSA-N 0.000 title claims abstract description 134
- 229910052753 mercury Inorganic materials 0.000 title claims abstract description 131
- 238000000034 method Methods 0.000 title claims abstract description 87
- 239000002699 waste material Substances 0.000 title claims abstract description 40
- 238000011084 recovery Methods 0.000 title claims abstract description 39
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 130
- 239000011521 glass Substances 0.000 claims abstract description 121
- 238000005406 washing Methods 0.000 claims abstract description 57
- 239000006228 supernatant Substances 0.000 claims abstract description 5
- 238000003860 storage Methods 0.000 claims description 21
- 238000003756 stirring Methods 0.000 claims description 19
- 238000004064 recycling Methods 0.000 claims description 10
- 239000000463 material Substances 0.000 claims description 9
- 239000007788 liquid Substances 0.000 claims description 5
- 238000001035 drying Methods 0.000 claims description 2
- 238000012545 processing Methods 0.000 abstract description 18
- 238000003672 processing method Methods 0.000 abstract description 2
- 239000012530 fluid Substances 0.000 abstract 1
- 230000001376 precipitating effect Effects 0.000 abstract 1
- 238000004140 cleaning Methods 0.000 description 21
- OAICVXFJPJFONN-UHFFFAOYSA-N Phosphorus Chemical compound [P] OAICVXFJPJFONN-UHFFFAOYSA-N 0.000 description 16
- 230000000694 effects Effects 0.000 description 9
- 239000002440 industrial waste Substances 0.000 description 9
- CDBYLPFSWZWCQE-UHFFFAOYSA-L Sodium Carbonate Chemical compound [Na+].[Na+].[O-]C([O-])=O CDBYLPFSWZWCQE-UHFFFAOYSA-L 0.000 description 5
- 239000000843 powder Substances 0.000 description 5
- UCKMPCXJQFINFW-UHFFFAOYSA-N Sulphide Chemical compound [S-2] UCKMPCXJQFINFW-UHFFFAOYSA-N 0.000 description 4
- 239000003795 chemical substances by application Substances 0.000 description 4
- 239000010802 sludge Substances 0.000 description 4
- 239000000243 solution Substances 0.000 description 4
- 229910052788 barium Inorganic materials 0.000 description 3
- DSAJWYNOEDNPEQ-UHFFFAOYSA-N barium atom Chemical compound [Ba] DSAJWYNOEDNPEQ-UHFFFAOYSA-N 0.000 description 3
- 239000002585 base Substances 0.000 description 3
- 230000002950 deficient Effects 0.000 description 3
- 238000010586 diagram Methods 0.000 description 3
- 238000010438 heat treatment Methods 0.000 description 3
- 238000004519 manufacturing process Methods 0.000 description 3
- 239000000047 product Substances 0.000 description 3
- 239000000126 substance Substances 0.000 description 3
- 229910000497 Amalgam Inorganic materials 0.000 description 2
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 2
- GRYLNZFGIOXLOG-UHFFFAOYSA-N Nitric acid Chemical compound O[N+]([O-])=O GRYLNZFGIOXLOG-UHFFFAOYSA-N 0.000 description 2
- ATUOYWHBWRKTHZ-UHFFFAOYSA-N Propane Chemical compound CCC ATUOYWHBWRKTHZ-UHFFFAOYSA-N 0.000 description 2
- FPWJLQXCGHQXLL-UHFFFAOYSA-N [P].OP(O)(O)=O Chemical compound [P].OP(O)(O)=O FPWJLQXCGHQXLL-UHFFFAOYSA-N 0.000 description 2
- 239000003463 adsorbent Substances 0.000 description 2
- 229910052783 alkali metal Inorganic materials 0.000 description 2
- 150000001340 alkali metals Chemical class 0.000 description 2
- 229910052784 alkaline earth metal Inorganic materials 0.000 description 2
- 150000001342 alkaline earth metals Chemical class 0.000 description 2
- 239000013522 chelant Substances 0.000 description 2
- 239000000470 constituent Substances 0.000 description 2
- 230000007423 decrease Effects 0.000 description 2
- 230000007613 environmental effect Effects 0.000 description 2
- 239000007789 gas Substances 0.000 description 2
- 229910052736 halogen Inorganic materials 0.000 description 2
- 150000002367 halogens Chemical class 0.000 description 2
- -1 mercury sulfide compound Chemical class 0.000 description 2
- 229910017604 nitric acid Inorganic materials 0.000 description 2
- 230000001737 promoting effect Effects 0.000 description 2
- 229910052761 rare earth metal Inorganic materials 0.000 description 2
- 150000002910 rare earth metals Chemical class 0.000 description 2
- 239000011347 resin Substances 0.000 description 2
- 229920005989 resin Polymers 0.000 description 2
- 229920006395 saturated elastomer Polymers 0.000 description 2
- 238000012546 transfer Methods 0.000 description 2
- 102100033041 Carbonic anhydrase 13 Human genes 0.000 description 1
- MYMOFIZGZYHOMD-UHFFFAOYSA-N Dioxygen Chemical compound O=O MYMOFIZGZYHOMD-UHFFFAOYSA-N 0.000 description 1
- 101000867860 Homo sapiens Carbonic anhydrase 13 Proteins 0.000 description 1
- DGAQECJNVWCQMB-PUAWFVPOSA-M Ilexoside XXIX Chemical compound C[C@@H]1CC[C@@]2(CC[C@@]3(C(=CC[C@H]4[C@]3(CC[C@@H]5[C@@]4(CC[C@@H](C5(C)C)OS(=O)(=O)[O-])C)C)[C@@H]2[C@]1(C)O)C)C(=O)O[C@H]6[C@@H]([C@H]([C@@H]([C@H](O6)CO)O)O)O.[Na+] DGAQECJNVWCQMB-PUAWFVPOSA-M 0.000 description 1
- 235000002597 Solanum melongena Nutrition 0.000 description 1
- 244000061458 Solanum melongena Species 0.000 description 1
- NINIDFKCEFEMDL-UHFFFAOYSA-N Sulfur Chemical compound [S] NINIDFKCEFEMDL-UHFFFAOYSA-N 0.000 description 1
- 239000007864 aqueous solution Substances 0.000 description 1
- 230000001112 coagulating effect Effects 0.000 description 1
- 238000007796 conventional method Methods 0.000 description 1
- 238000001816 cooling Methods 0.000 description 1
- 239000006063 cullet Substances 0.000 description 1
- 238000011161 development Methods 0.000 description 1
- 238000009792 diffusion process Methods 0.000 description 1
- 229910001882 dioxygen Inorganic materials 0.000 description 1
- 238000004090 dissolution Methods 0.000 description 1
- 238000007922 dissolution test Methods 0.000 description 1
- 238000004821 distillation Methods 0.000 description 1
- 239000010791 domestic waste Substances 0.000 description 1
- 239000000428 dust Substances 0.000 description 1
- 238000010828 elution Methods 0.000 description 1
- 238000007496 glass forming Methods 0.000 description 1
- 238000005286 illumination Methods 0.000 description 1
- 238000011835 investigation Methods 0.000 description 1
- 239000005355 lead glass Substances 0.000 description 1
- 238000005259 measurement Methods 0.000 description 1
- 238000002844 melting Methods 0.000 description 1
- 230000008018 melting Effects 0.000 description 1
- 150000002730 mercury Chemical class 0.000 description 1
- 238000001556 precipitation Methods 0.000 description 1
- 239000001294 propane Substances 0.000 description 1
- 238000007789 sealing Methods 0.000 description 1
- 238000004062 sedimentation Methods 0.000 description 1
- 229910052708 sodium Inorganic materials 0.000 description 1
- 239000011734 sodium Substances 0.000 description 1
- 229910052717 sulfur Inorganic materials 0.000 description 1
- 239000011593 sulfur Substances 0.000 description 1
- 238000010998 test method Methods 0.000 description 1
- WFKWXMTUELFFGS-UHFFFAOYSA-N tungsten Chemical compound [W] WFKWXMTUELFFGS-UHFFFAOYSA-N 0.000 description 1
- 229910052721 tungsten Inorganic materials 0.000 description 1
- 239000010937 tungsten Substances 0.000 description 1
Classifications
-
- 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
- Y02W30/50—Reuse, recycling or recovery technologies
- Y02W30/82—Recycling of waste of electrical or electronic equipment [WEEE]
Landscapes
- Processing Of Solid Wastes (AREA)
Abstract
Description
【0001】[0001]
【発明の属する技術分野】本発明は、廃蛍光ランプ、特
に使用済ランプの水銀回収方法とその装置に関するもの
である。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method and apparatus for recovering mercury from waste fluorescent lamps, particularly used lamps.
【0002】[0002]
【従来の技術】省エネルギー時代を迎えて、蛍光ランプ
は照明用光源のなかでも特長として高いランプ効率を有
することから、今後とも主力光源としての需要の伸びが
期待されている。2. Description of the Related Art With the advent of an energy-saving era, fluorescent lamps have high lamp efficiency as a feature among illumination light sources, and thus demand for main light sources is expected to grow.
【0003】一方、最近の地球環境保護のために、製品
に使われる有害物質の回収や部材のリサイクル使用が要
望されている。ここで、蛍光ランプに基本構成部材とし
て封入されている紫外放射物質である水銀は有害物質で
あることから、近年は廃蛍光ランプ及び関連部材の廃棄
処理やリサイクル使用に際して、特にその無公害化のた
めに封入水銀の回収による除去が求められるようになっ
た。On the other hand, in recent years, in order to protect the global environment, there is a demand for recovery of harmful substances used in products and recycling of members. Here, since mercury, which is an ultraviolet radiating substance enclosed as a basic constituent member in a fluorescent lamp, is a harmful substance, in recent years, especially when the waste fluorescent lamp and related members are disposed of or recycled and used, no pollution is required. Therefore, the removal of the enclosed mercury by recovery has been required.
【0004】従来の廃蛍光ランプは、その廃棄処理にあ
たり2つの廃棄物カテゴリー、すなわち(a)一般家庭
などでの使用済蛍光ランプである一般廃棄物と、(b)
一般ビルオフィスや工場での使用済蛍光ランプ及び製造
工程における製造不良ランプなどである産業廃棄物に分
類されている。そして、前者の一般廃棄物の多くは、現
在のところ不燃物の一般家庭ゴミと同様の埋立処理がな
されている。一方、後者の産業廃棄物である廃蛍光ラン
プ及び関連部材は、1973年2月17日の環境庁告示
第13号規定の溶出試験方法で、溶出液中の水銀量とし
て基準値0.005mg/リットル以下であることが求め
られている。ここで、含有水銀量が上記基準値以上の産
業廃棄物は、無害化処理をするか特別に管理された埋立
地へ搬送して処理するよう規定されている。The conventional waste fluorescent lamp has two waste categories for its disposal, namely (a) general waste which is a used fluorescent lamp in general households, and (b).
It is classified into industrial waste such as used fluorescent lamps in general building offices and factories and defective lamps in the manufacturing process. Most of the former general waste is currently landfilled like non-combustible general household waste. On the other hand, the latter industrial waste, such as waste fluorescent lamps and related components, was subjected to the elution test method specified by the Environmental Agency Notification No. 13 on February 17, 1973, and the standard value of mercury in the eluate was 0.005 mg / It is required to be liter or less. Here, it is stipulated that industrial waste containing mercury above the standard value should be detoxified or transported to a specially controlled landfill for disposal.
【0005】産業廃棄物として水銀回収が求められてい
る廃蛍光ランプは、前記のように、市場での使用済蛍光
ランプと製造工程における製造不良ランプである。更
に、廃蛍光ランプの関連部材としては、製造工程で使用
される排気用の細管ガラスが挙げられる。そして、かか
る廃蛍光ランプ及び関連部材の水銀回収方法は、従来か
ら広く検討されており、例えば特開昭52−33387
号公報、特開昭54−137426号公報、特開平6−
154641号公報、特開平8−168747号公報、
特開平10−12149号公報、特開平11−2073
13号公報、特開2000−202319号公報、特開
2000−215811号公報、特開2000−303
125号公報、特開2001−11548号公報、特開
2001−81449号公報などに提案されている。As mentioned above, the waste fluorescent lamps that are required to recover mercury as industrial wastes are used fluorescent lamps on the market and defective lamps in the manufacturing process. Further, as a related member of the waste fluorescent lamp, there is a thin glass tube for exhaust used in the manufacturing process. The mercury recovery method for such waste fluorescent lamps and related members has been widely studied in the past, and is disclosed in, for example, JP-A-52-33387.
JP-A-54-137426, JP-A-6-
Japanese Patent No. 154641, Japanese Patent Application Laid-Open No. 8-168747,
JP-A-10-12149, JP-A-11-2073
No. 13, JP-A-2000-202319, JP-A-2000-215811, and JP-A-2000-303.
No. 125, JP 2001-11548 A, JP 2001-81449 A, etc. are proposed.
【0006】ところで、蛍光ランプの構成部材は、上記
封入水銀のほかに、(i)発光管を形成する発光管ガラ
ス、(ii)一対のタングステンコイル電極部を保持して
管両端に気密封着されたステムガラス及びこれに装着さ
れた口金、(iii)管内表面に塗布された蛍光体、から
なっている。そして、前記廃蛍光ランプにおける封入水
銀は、特に上記(iii)の蛍光体に多く付着・含有され
ている。従って、従来技術で一般に適用されてきた廃蛍
光ランプの処理工程では、最初にランプは発光管ガラ
ス、蛍光体及び口金付ステムガラス(但し、一部蛍光体
も混入)の3つの部材に分離され、次いで各部材の水銀
回収にはそれぞれに適合した方法が採用されてきた。The constituent members of the fluorescent lamp are, in addition to the enclosed mercury, (i) an arc tube glass forming the arc tube, (ii) holding a pair of tungsten coil electrode portions and hermetically sealing the both ends of the tube. The formed stem glass, the base attached to the stem glass, and (iii) the phosphor coated on the inner surface of the tube. Further, the enclosed mercury in the waste fluorescent lamp is attached and contained in a large amount particularly in the phosphor of (iii) above. Therefore, in the treatment process of a waste fluorescent lamp which has been generally applied in the prior art, the lamp is first separated into three members, that is, an arc tube glass, a phosphor and a stem glass with a base (however, some phosphor is mixed). Then, a method adapted to each has been adopted for the mercury recovery of each member.
【0007】なお、従来蛍光ランプの上記発光ガラス及
びステムガラスとして、それぞれ主にソーダガラス及び
鉛ガラスが用いられてきた。但し、最近は蛍光ランプの
効率や寿命特性の改善のために、発光管ガラスにはソー
ダガラスに代ってナトリウムフリーのバリウム系ガラス
等も用いられている。Conventionally, soda glass and lead glass have been mainly used as the above-mentioned light-emitting glass and stem glass of fluorescent lamps, respectively. However, recently, sodium-free barium-based glass or the like has been used as the arc tube glass in place of soda glass in order to improve the efficiency and life characteristics of fluorescent lamps.
【0008】従来技術による廃蛍光ランプ及び関連部材
の水銀回収方法は、大きく乾式と湿式の2つに分類でき
る。The method of recovering mercury from waste fluorescent lamps and related members according to the prior art can be roughly classified into two types: dry type and wet type.
【0009】前者の乾式方法としては、基本的にまず廃
蛍光ランプ部材及び細管ガラス部材を大気圧あるいは真
空も含む減圧の装置内で加熱してその付着・含有水銀を
水銀蒸気として分離し、次いで前記水銀蒸気を(a)冷
却凝集して回収するか、あるいは(b)活性炭やキレー
ト樹脂などの水銀吸着材により吸着・除去する、という
方法が一般に広く適用されてきた。As the former dry method, basically, the waste fluorescent lamp member and the thin tube glass member are first heated in a depressurized apparatus including atmospheric pressure or vacuum to separate the attached / contained mercury as mercury vapor, and then A method of (a) cooling and coagulating and collecting the mercury vapor or (b) adsorbing and removing the mercury vapor with a mercury adsorbent such as activated carbon or a chelate resin has been widely applied.
【0010】一方、後者の湿式方法としては、例えば
(a)一旦破砕した廃蛍光ランプ部材を希硝酸などの水
銀溶解液に侵漬してその付着・含有水銀を溶解により分
離して、次いでかかる水銀溶解液中に溶解した水銀をキ
レート樹脂などの水銀吸着材により吸着して回収する、
あるいは(b)破砕した廃蛍光ランプ部材を活性硫黄を
主体とした硫化物処理剤等の水溶液に接触させて、その
付着・含有水銀を水に難溶性の硫化水銀化合物等として
回収する、という方法等が開示され適用されてきた。ま
た、特に関連の細管ガラス部材に関しては、まず破砕し
た細管ガラスの水洗浄と浮遊洗浄水槽への侵漬によりそ
の付着水銀を遊離水銀として分離し、次いでかかる洗浄
水と浮遊洗浄水槽中の遊離水銀を沈降させて回収する、
という方法が提案されている。On the other hand, as the latter wet method, for example, (a) the once crushed waste fluorescent lamp member is immersed in a mercury solution such as dilute nitric acid to separate the adhered / contained mercury by dissolution, and then the following method is applied. Mercury dissolved in mercury solution is adsorbed and recovered by a mercury adsorbent such as chelate resin.
Alternatively, (b) a method in which a crushed waste fluorescent lamp member is brought into contact with an aqueous solution of a sulfide treating agent containing active sulfur as a main component, and the mercury adhering to and contained therein is recovered as a water-insoluble mercury sulfide compound or the like. Etc. have been disclosed and applied. In addition, regarding the related thin glass tube members, first, the crushed thin glass is washed with water and immersed in a floating cleaning water tank to separate the attached mercury as free mercury, and then such cleaning water and free mercury in the floating cleaning water tank are separated. Is collected by sedimentation,
That method has been proposed.
【0011】[0011]
【発明が解決しようとする課題】今後、地球環境保護へ
の取組みが加速されるなかで、一般廃棄物も含めた廃蛍
光ランプの水銀回収を徹底して、特にその部材のリサイ
クル使用が一層要望されることは確かである。As efforts to protect the global environment are accelerated in the future, it will be even more desirable to thoroughly collect mercury from waste fluorescent lamps, including general waste, and to recycle the members. It is certain that it will be done.
【0012】本発明者らによる廃蛍光ランプのリサイク
ル使用状況の調査によれば、現時点では主に産業廃棄物
のうちの製造不良ランプ及び細管ガラスの発光管ガラス
部材と一部蛍光体部材がリサイクル使用されているにす
ぎない。従って、今後の主要課題は、特に廃蛍光ランプ
の大部分を占める一般廃棄物も含めた使用済蛍光ランプ
の部材、その中でも使用部材量が最大の発光管ガラス部
材のリサイクル使用を進捗させることである。According to the present inventors' investigation of the recycling and use status of waste fluorescent lamps, at present, mainly incompletely manufactured lamps of industrial waste, arc tube glass members of thin tube glass and some phosphor members are recycled. It is only used. Therefore, the main issue in the future is to progress the recycling of the used fluorescent lamp members, including the general waste that occupies most of the waste fluorescent lamps, among them, the arc tube glass member with the largest amount of used members. is there.
【0013】本発明者らは、上記背景を踏まえて、特に
使用済蛍光ランプの発光管ガラス部材のリサイクル使用
を進めるうえに必要な水銀回収方法とそれを適用した装
置の開発に取組んだ。Based on the above background, the present inventors have made efforts to develop a mercury recovery method and an apparatus to which the method is applied, which is particularly necessary for promoting the recycling and use of arc tube glass members of used fluorescent lamps.
【0014】本発明者らは、まず前記従来技術のなかか
ら、本開発での上記発光管ガラス部材のリサイクル使用
に適合する水銀回収方法を探索した。この場合、その適
合条件として、(a)第1に上記発光管ガラスの含有水銀
量を前記基準値0.005mg/リットル以下のレベルま
で除去できる、(b)本開発の対象とする使用済蛍光ラ
ンプ処理の進捗を図るために、その処理工程及び設備が
比較的簡易で処理コストを低くできる、(c)処理工程に
おける作業環境が安全である、という3つを設定した。The inventors of the present invention first searched for a mercury recovery method suitable for the recycling use of the arc tube glass member in the present development from the above-mentioned conventional techniques. In this case, the applicable conditions are (a) first, the amount of mercury contained in the arc tube glass can be removed to a level below the standard value of 0.005 mg / liter, (b) used fluorescent light to be developed In order to improve the progress of the lamp treatment, we have set three factors: the treatment process and equipment are relatively simple, the treatment cost can be reduced, and (c) the work environment in the treatment process is safe.
【0015】ところが、結果として前記従来技術による
いずれの水銀回収方法も3つの上記適合条件を満たし得
ないことがわかった。例えば、従来製造不良ランプの処
理には広く適用されてきた“加熱から水銀蒸気の回収”
という前記乾式方法は、特に上記条件(a)を満たし得
なかった。また、水銀溶解液や硫化物処理剤等による湿
式方法は、特に上記条件(b)及び(c)を満たし得なか
った。また、細管ガラス部材処理用の単なる水洗浄等に
よる湿式方法も、上記条件(a)を到底満たすものでな
かった。However, as a result, it has been found that none of the above-mentioned conventional mercury recovery methods can satisfy the above-mentioned three conforming conditions. For example, “Recovery of mercury vapor from heating” that has been widely applied to the treatment of defective lamps.
The above dry method could not satisfy the above condition (a). Further, the wet method using a mercury solution or a sulfide treating agent could not satisfy the above conditions (b) and (c). Further, the wet method such as mere washing with water for treating the thin tube glass member does not satisfy the above condition (a) at all.
【0016】以上のように、今後使用済蛍光ランプの発
光管ガラス部材のリサイクル使用を進捗するには、まず
上記3つの適合条件を満たす水銀処理方法を見い出し、
次いでそれを適用した処理工程及び設備を考案する、こ
とが主要な技術課題である。As described above, in order to make progress in the recycling and use of arc tube glass members of used fluorescent lamps in the future, first, a mercury treatment method satisfying the above three conformity conditions is found,
The next major technical issue is to devise a treatment process and equipment to which it is applied.
【0017】本発明は、廃蛍光ランプ、特に使用済蛍光
ランプの発光管ガラス部材の水銀回収処理において、発
光管ガラスの含有水銀量を前記基準値0.005mg/リ
ットル以下のレベルまで回収・除去でき、かつ低処理コ
ストで作業環境も安全な水銀回収方法を見い出して、こ
れを適用することにより前記発光管ガラス部材のリサイ
クル使用を進捗するような処理方法及び装置を提供する
ことを目的とする。According to the present invention, in the mercury recovery treatment of the arc tube glass member of a waste fluorescent lamp, particularly a used fluorescent lamp, the mercury content of the arc tube glass is recovered / removed to a level of 0.005 mg / liter or less. An object of the present invention is to find a mercury recovery method that can be carried out at a low processing cost and a safe working environment, and by applying the method, a processing method and an apparatus that can promote the recycle use of the arc tube glass member. .
【0018】[0018]
【課題を解決するための手段】前記目的を達成するた
め、本発明の廃蛍光ランプの水銀回収方法は、廃蛍光ラ
ンプから分離された発光管ガラス部材から水銀を回収す
る方法であって、前記発光管ガラス部材を破砕し、前記
破砕物を温水洗浄機に投入して温水とともに攪拌し、ガ
ラス破砕物と水銀に分離し、前記分離された水銀は温水
とともに貯槽に入れ、前記貯槽の下部に沈殿させて回収
し、前記ガラス破砕物は乾燥して取り出し、前記貯槽の
上澄み液の温水はリサイクルして温水洗浄機に供給する
ことを特徴とする。In order to achieve the above object, a method for recovering mercury from a waste fluorescent lamp according to the present invention is a method for recovering mercury from an arc tube glass member separated from a waste fluorescent lamp. The arc tube glass member is crushed, the crushed product is put into a warm water washing machine and stirred with warm water, and the crushed glass and mercury are separated, and the separated mercury is put in a storage tank together with hot water, and is stored in the lower part of the storage tank. It is characterized in that it is precipitated and recovered, the crushed glass is dried and taken out, and the warm water of the supernatant liquid of the storage tank is recycled and supplied to a warm water washing machine.
【0019】次に本発明の廃蛍光ランプの水銀回収装置
廃蛍光ランプから分離された発光管ガラス部材から水銀
を回収する装置であって、前記発光管ガラス部材を破砕
する手段と、前記破砕物を温水洗浄機に投入する手段
と、前記温水洗浄機に温水を供給する手段と、ガラス破
砕物と水銀に分離するための攪拌手段とを備え、前記分
離された水銀を温水とともに貯槽に入れ、前記貯槽の下
部に沈殿させて回収する手段と、前記ガラス破砕物を乾
燥して取り出す手段と、前記貯槽の上澄み液の温水はリ
サイクルして温水洗浄機に供給する手段を備えたことを
特徴とする。Next, the mercury recovery apparatus for the waste fluorescent lamp of the present invention is an apparatus for recovering mercury from the arc tube glass member separated from the waste fluorescent lamp, the means for crushing the arc tube glass member, and the crushed material. Means for charging the hot water washer, means for supplying hot water to the hot water washer, and a stirring means for separating glass crushed material and mercury, put the separated mercury in a storage tank together with hot water, The apparatus further comprises means for collecting the glass crushed product by precipitation in the lower part of the storage tank, means for drying and taking out the crushed glass, and means for recycling hot water of the supernatant liquid of the storage tank and supplying it to a hot water washing machine. To do.
【0020】これにより、基本的に前記発光管ガラス部
材の含有水銀量を規定基準値0.005mg/リットル以
下のレベルまで回収・除去でき、かつ低処理コストと安
全な作業環境も得られ、よってこの水銀回収方法を適用
することにより前記発光管ガラス部材のリサイクル使用
を進捗するような方法及び装置が具現できる。As a result, basically, the amount of mercury contained in the glass member of the arc tube can be recovered / removed to a level below the specified standard value of 0.005 mg / liter, and a low processing cost and a safe working environment can be obtained. By applying this mercury recovery method, it is possible to implement a method and apparatus for promoting the recycling use of the arc tube glass member.
【0021】[0021]
【発明の実施の形態】本発明においては、前記温水洗浄
処理に用いられる温水の温度が、35℃以上の範囲であ
ることが好ましい。これにより、前記発光管ガラス部材
の含有水銀量を規定基準値0.005mg/リットル以
下、更に好ましくは0.002mg/リットル以下のレベ
ルまで回収・除去でき、前記発光管ガラス部材のリサイ
クル使用が可能となる。前記温水の温度は、さらに40
℃以上80℃以下の範囲が好ましい。BEST MODE FOR CARRYING OUT THE INVENTION In the present invention, it is preferable that the temperature of the hot water used for the hot water washing treatment is in the range of 35 ° C. or higher. As a result, the amount of mercury contained in the arc tube glass member can be recovered / removed to a level of a specified standard value of 0.005 mg / liter or less, more preferably 0.002 mg / liter or less, and the arc tube glass member can be recycled. Becomes The temperature of the hot water is 40
It is preferably in the range of ℃ to 80 ℃.
【0022】また本発明においては、前記攪拌機付温水
洗浄機における処理が、バッチ式または連続式であるこ
とが好ましい。Further, in the present invention, it is preferable that the treatment in the warm water washing machine with a stirrer is a batch type or a continuous type.
【0023】また本発明においては、前記温水洗浄機に
おける攪拌手段が、攪拌機による攪拌または前記温水洗
浄機の槽が回転することによる攪拌であることが好まし
い。Further, in the present invention, it is preferable that the stirring means in the hot water washing machine is stirring by a stirrer or by rotating a tank of the hot water washing machine.
【0024】これにより、前記発光管ガラス部材の含有
水銀量を規定基準値0.005mg/リットル以下のレベ
ルまで回収・除去でき、かつ低処理コストと安全な作業
環境も得られ、併せて前記温水洗浄による処理時間が短
縮された高能率の前記発光管ガラス部材の処理方法及び
装置が具現できる。As a result, the amount of mercury contained in the glass member of the arc tube can be recovered / removed to a level of 0.005 mg / liter or less of the standard value, and a low processing cost and a safe working environment can be obtained. It is possible to implement a highly efficient method and apparatus for processing the glass member of the arc tube in which the processing time by cleaning is shortened.
【0025】以下、本発明の実施の形態を図1から図4
を用いて説明する。Hereinafter, an embodiment of the present invention will be described with reference to FIGS.
Will be explained.
【0026】(実施の形態1)図1は、本発明の実施の
形態1である使用済蛍光ランプの発光管ガラス部材の水
銀回収方法と、それを適用した特に発光管ガラス部材の
処理装置の全体構成を示す。使用済蛍光ランプ1は、ま
ずプロパンガスと酸素ガスの混合ガスバーナーにより管
両端の口金付ステムガラス部材2、3が切断・分離さ
れ、次いで高圧エアーブローにより発光管ガラス部材4
の内面に塗布されている蛍光体5部材が剥離・分離され
る。そして、残りの本発明に関連する発光管ガラス4部
材が、下記の本実施形態1である水銀回収方法を適用し
た処理工程及び設備により処理されることになる。(Embodiment 1) FIG. 1 shows a method for recovering mercury from an arc tube glass member of a used fluorescent lamp, which is Embodiment 1 of the present invention, and an apparatus for treating the arc tube glass member, to which the method is applied. The overall configuration is shown. In the used fluorescent lamp 1, first, stem glass members 2 and 3 with caps at both ends of the tube are cut and separated by a mixed gas burner of propane gas and oxygen gas, and then the arc tube glass member 4 by high pressure air blow.
The phosphor 5 member coated on the inner surface of is removed and separated. Then, the remaining arc tube glass 4 member related to the present invention is treated by the treatment process and equipment to which the mercury recovery method according to the first embodiment described below is applied.
【0027】なお、分離された上記口金付ステムガラス
部材2、3は、加熱炉(図示せず)での加熱処理により
一部水銀が回収・除去された後に、産業廃棄物として無
害化処理されるか特別に管理された埋立地に搬送・処理
される。また、前記のように水銀を多く含む上記蛍光体
部材5は、粉体として一旦回収され、次いでかかる粉体
に含まれる水銀が水銀蒸留装置(図示せず)により回収
され、残余の粉体をなす蛍光体部材5が産業廃棄物とし
て同様に処理される。ここで、水銀蒸留装置により回収
された水銀は、そのまま蛍光ランプ用としてリサイクル
使用される。The separated stem glass members 2 and 3 with a cap are detoxified as industrial waste after a part of mercury is recovered and removed by a heating process in a heating furnace (not shown). Or transported to a specially managed landfill site. Further, as described above, the phosphor member 5 containing a large amount of mercury is once recovered as a powder, and then the mercury contained in the powder is recovered by a mercury distilling device (not shown) to remove the remaining powder. The eggplant phosphor member 5 is similarly treated as industrial waste. Here, the mercury recovered by the mercury distillation apparatus is recycled and used as it is for fluorescent lamps.
【0028】本発明者らは、図1の使用済蛍光ランプ1
の発光管ガラス部材4の処理工程及び装置の開発にあた
り、特にその発光管ガラス部材4からの水銀回収方法を
探索し検討した。この結果、特に下記のように使用済蛍
光ランプ1の破砕した発光管ガラス部材4を基本的に温
水洗浄する、という水銀回収方法が前記3つの適合条件
を満たし得ることを見い出した。The present inventors have used the used fluorescent lamp 1 of FIG.
In developing the treatment process and apparatus for the arc tube glass member 4, the method for recovering mercury from the arc tube glass member 4 was searched and studied. As a result, it has been found that a mercury recovery method, in which the crushed arc tube glass member 4 of the used fluorescent lamp 1 is basically washed with warm water as described below, can satisfy the above-mentioned three compatible conditions.
【0029】発光管ガラス部材4の一連の処理工程とし
ては、(i)発光管ガラス部材4がガラス破砕機6によ
り破砕され、(ii)破砕された発光管ガラス部材4が搬
送コンベアー7により温水洗浄機8に搬送・投入され、
(iii)発光管ガラス部材4の含有水銀が本実施形態1
である温水洗浄機8内での洗浄処理により前記基準値
0.005mg/リットル以下のレベルまで除去され、(i
v)水銀の除去された発光管ガラスは搬送コンベアー1
7により温風循環装置19を装備したロータリー乾燥機
18へと搬送・投入され、(v)最終的に発光管ガラス
部材4がここで乾燥され、ガラスコンテナー20へと回
収されることになる。そして、回収された発光管ガラス
部材4は、ガラス溶融炉用カレット、ガラスタイル、道
路用路盤材などにそのままリサイクル使用できる。As a series of processing steps of the arc tube glass member 4, (i) the arc tube glass member 4 is crushed by the glass crusher 6, and (ii) the crushed arc tube glass member 4 is heated by the transport conveyor 7 into hot water. Transported and put into the washing machine 8,
(Iii) The mercury contained in the arc tube glass member 4 is present in the first embodiment.
Is removed to a level of 0.005 mg / liter or less by the washing treatment in the warm water washing machine 8, which is (i
v) Conveyor 1 for arc tube glass from which mercury has been removed
It is conveyed and thrown into the rotary dryer 18 equipped with the warm air circulation device 19 by (7), and (v) the arc tube glass member 4 is finally dried here and collected in the glass container 20. Then, the recovered arc tube glass member 4 can be recycled and used as it is for a cullet for a glass melting furnace, a glass tile, a roadbed material for a road, and the like.
【0030】上記本実施形態1である水銀回収方法を適
用した上記(iii)の処理工程及び設備を詳しく説明す
ると、まず温水洗浄機8の下部には貯槽9が備えられ、
これには温水循環ポンプ21が付設され、温水循環ライ
ン10より温度制御された温水が上側の給水管11から
注入される。また、温水洗浄機8にはモーター回転され
る撹拌翼12も取り付けられ、温水に浸漬された発光管
ガラス部材4は撹拌・処理されている。ここで、下記の
ように、攪拌翼12は温水洗浄の処理時間を短縮するた
めに設置されている。温水洗浄機の直径が150cm、
高さが200cm、処理量3500リットルの場合、攪
拌機の回転数は3〜5rpmが好ましく、処理時間は2
0分程度が好ましい。The process step (iii) and equipment to which the mercury recovery method of the first embodiment is applied will be described in detail. First, a storage tank 9 is provided below the warm water washing machine 8,
A hot water circulation pump 21 is attached to this, and hot water whose temperature is controlled is injected from the hot water circulation line 10 through the upper water supply pipe 11. A stirring blade 12 that is rotated by a motor is also attached to the warm water washing machine 8, and the arc tube glass member 4 immersed in warm water is stirred and treated. Here, as described below, the stirring blade 12 is installed in order to shorten the processing time for washing with warm water. The diameter of the hot water washing machine is 150 cm,
When the height is 200 cm and the treatment amount is 3500 liters, the rotation speed of the stirrer is preferably 3 to 5 rpm, and the treatment time is 2
About 0 minutes is preferable.
【0031】また、本実施形態1による温水洗浄の処理
工程では、特に所定量の発光管ガラス部材4が温水洗浄
機8内に一度に投入され、いわゆるバッチ方式による水
銀回収・処理がなされており、処理された発光管ガラス
部材4はバッチ処理毎のシャッター13の開放により温
水とともに下側開口部14を通じて前記搬送コンベアー
17へと移送される。一方、同時に温水は温水ホッパー
15を経て前記貯槽9内に一旦回収・処理されて、これ
が再び温度制御された温水として前記給水管11へと供
給される。ここで、貯槽9に一旦回収された温水に含ま
れている水銀は、貯槽9の底部に蛍光体及びガラス粉体
クズとともに沈積し、かかる水銀を含む沈積物がパンケ
ーキ状の汚泥物16として回収される。そして、この汚
泥物16は産業廃棄物として無害化処理するか特別に管
理された埋立地へ搬送・処理される。Further, in the hot water washing treatment step according to the first embodiment, particularly, a predetermined amount of the arc tube glass member 4 is put into the hot water washing machine 8 at a time, and so-called batch type mercury recovery / treatment is performed. The processed arc tube glass member 4 is transferred to the transfer conveyor 17 through the lower opening 14 together with warm water by opening the shutter 13 for each batch processing. On the other hand, at the same time, the hot water is once collected and processed in the storage tank 9 through the hot water hopper 15, and is again supplied to the water supply pipe 11 as the temperature-controlled hot water. Here, the mercury contained in the hot water once collected in the storage tank 9 is deposited on the bottom of the storage tank 9 together with the phosphor and the glass powder waste, and the deposit containing the mercury is converted into pancake-like sludge 16. Be recovered. Then, the sludge 16 is detoxified as industrial waste or transported / treated to a specially managed landfill.
【0032】なお、上記バッチ処理毎の使用済蛍光ラン
プの処理灯数は、例えば直径1.5m/深長2.0mの円筒
形の温水洗浄機8を用いたとき、40Wタイプで約40
00灯であった。The number of used fluorescent lamps for each batch treatment is about 40 in 40 W type when using a cylindrical hot water washing machine 8 having a diameter of 1.5 m / deep length of 2.0 m, for example.
It was 00 lights.
【0033】上記本実施形態1である水銀回収方法の特
徴は、発光管ガラス部材4の含有水銀を回収・除去する
のに温水洗浄を採用したことである。The characteristic of the mercury recovery method of the first embodiment is that hot water cleaning is adopted to recover and remove the mercury contained in the arc tube glass member 4.
【0034】本発明者らは、使用済蛍光ランプ1の発光
管ガラス部材4の水銀回収方法を探索・検討するなか
で、温水洗浄処理に注目し、特に処理に用いる温水の温
度と洗浄処理時間の2つのパラメータを変えたときの含
有水銀の回収・除去効果を調べた。この結果、図2に示
すように、特に温水の温度が含有水銀の回収・除去効果
に密接に関係していることを見い出した。The inventors of the present invention focused on hot water washing treatment while searching for and examining a method of recovering mercury from the arc tube glass member 4 of the used fluorescent lamp 1, and particularly focused on the temperature of hot water used for the treatment and the washing treatment time. The effect of recovering / removing contained mercury when the two parameters were changed was investigated. As a result, as shown in FIG. 2, it was found that the temperature of the hot water is closely related to the effect of recovering and removing the contained mercury.
【0035】図2は、蛍光体部材5としてハロゲンリン
酸蛍光体及び3波長形希土類蛍光体がそれぞれ塗布され
たソーダガラスの発光管ガラス部材4に関して、上記本
実施形態1の水銀回収方法である温水洗浄で処理された
発光管ガラス部材4の含有水銀量(前記溶出試験方法に
よる値)と温水の温度との関係を示す。なお、この測定
では、温水洗浄機8に取り付けられた攪拌翼12は5r
pmで攪拌した。また、温水洗浄処理前の破砕された発
光管ガラス部材4の含有水銀量は、それぞれ0.031
mg/リットル及び0.032mg/リットルであった。FIG. 2 shows the mercury recovery method according to the first embodiment with respect to the soda glass arc tube glass member 4 coated with a halogen phosphoric acid phosphor and a three-wavelength rare earth phosphor as the phosphor member 5. The relationship between the amount of mercury contained in the arc tube glass member 4 treated by washing with warm water (value according to the dissolution test method) and the temperature of warm water is shown. In addition, in this measurement, the stirring blade 12 attached to the warm water washer 8 was 5r.
Stirred at pm. The amount of mercury contained in the crushed arc tube glass member 4 before the hot water washing treatment was 0.031 each.
mg / liter and 0.032 mg / liter.
【0036】図2の結果から、その含有水銀量は、使用
蛍光体の種類にかかわらず温水の温度が常温20℃から
上昇するにつれて80℃までは減少し、次いで80℃以
上では飽和していくことが判明した。そして、常温20
℃付近のいわゆる単なる水洗浄では、特に使用済蛍光ラ
ンプ1の発光管ガラス部材4における含有水銀量の減少
・除去効果は小さいことがわかった。更に、温水10は
35℃以上、とくには40℃以上の温度範囲において、
発光管ガラス部材4の含有水銀量は前記基準値0.00
5mg/リットル以下のレベルまで確実に減少・除去し得
ることが明らかになった。From the results shown in FIG. 2, the mercury content decreases to 80 ° C. as the temperature of the hot water rises from 20 ° C. at room temperature, and then becomes saturated at 80 ° C. or higher, regardless of the type of phosphor used. It has been found. And room temperature 20
It was found that the effect of reducing / removing the amount of mercury contained in the arc tube glass member 4 of the used fluorescent lamp 1 is small by so-called simple water washing at around ° C. Further, the warm water 10 has a temperature range of 35 ° C or higher, particularly 40 ° C or higher,
The amount of mercury contained in the glass member 4 of the arc tube is the above-mentioned standard value of 0.00.
It has become clear that it can be reliably reduced / removed to a level of 5 mg / liter or less.
【0037】一方、特に温度を80℃より高めても含有
水銀の減少は飽和してくるので、処理工程での省エネル
ギー化の面から温度は80℃以下の範囲に保つのが適正
である。On the other hand, even if the temperature is raised above 80 ° C., the reduction of the contained mercury becomes saturated, so it is appropriate to keep the temperature within the range of 80 ° C. or less from the viewpoint of energy saving in the treatment process.
【0038】一方、もう一つのパラメータである洗浄処
理時間との関係を調べるまえに、まず温水洗浄機8に取
付けた攪拌翼12による攪拌効果を事前に調べた。この
結果、特に上記温水洗浄による処理時間を大幅に短縮で
きることがわかった。つまり、含有水銀量を同じ値まで
減少・除去するに要する洗浄処理時間は、温水洗浄機8
に取り付けられた撹拌翼12を撹拌したことにより、撹
拌しないときに比べて平均約1/3に短縮することがで
きた。On the other hand, before investigating the relationship with another parameter, that is, the cleaning treatment time, first, the stirring effect by the stirring blades 12 attached to the hot water cleaning machine 8 was investigated in advance. As a result, it was found that the treatment time by the above-mentioned washing with warm water can be greatly shortened. That is, the cleaning treatment time required to reduce / remove the contained mercury amount to the same value is 8
By stirring the stirring blades 12 attached to, it was possible to shorten the average to about 1/3 as compared with the case without stirring.
【0039】次いで、上記本実施形態1の構成に本来含
まれている拡散翼12を攪拌して、洗浄処理時間を5分
〜60分の範囲で変えたときの含有水銀量の減少割合を
測定した。この結果、図2に合わせて示されているよう
に、洗浄処理時間を長くすることによる含有水銀の減少
割合は、前記温水温度の上昇に比べて小さいことがわか
った。また、洗浄処理時間を10分以上に長くしたとき
の含有水銀の減少割合は比較的小さくなり、従って処理
工程の高能率化の面から洗浄処理時間は10分以下と短
くしてもよい。Next, the diffusion blade 12 originally included in the configuration of the first embodiment is stirred, and the reduction rate of the mercury content when the cleaning treatment time is changed within the range of 5 minutes to 60 minutes is measured. did. As a result, as shown in FIG. 2, it was found that the reduction rate of the contained mercury by prolonging the cleaning treatment time was smaller than the increase in the warm water temperature. Further, when the cleaning treatment time is increased to 10 minutes or longer, the reduction rate of the contained mercury becomes relatively small. Therefore, the cleaning treatment time may be shortened to 10 minutes or less from the viewpoint of improving the efficiency of the treatment process.
【0040】上記本実施形態1である水銀回収方法にお
いて、特に温水洗浄処理が発光管ガラス部材4の含有水
銀の減少・除去に有効であるのは、基本的に発光管ガラ
ス部材4の含有水銀は、主にその表面に偏析したナトリ
ウムなどのアルカリ金属あるいはバリウムなどのアルカ
リ土金属とアマルガムを生成して存在しており、かかる
アマルガム中の前記アルカリ金属あるいはアルカリ土金
属が単なる水よりも温水に溶解し易い、という性質に起
因するものである。In the mercury recovery method of the first embodiment described above, the fact that the hot water washing treatment is particularly effective for reducing and removing the mercury contained in the arc tube glass member 4 is basically the mercury contained in the arc tube glass member 4. Exists mainly by generating an amalgam with an alkali metal such as sodium segregated on its surface or an alkaline earth metal such as barium, and the alkali metal or alkaline earth metal in the amalgam is warm water rather than mere water. This is due to the property of being easily dissolved.
【0041】上記本発明による温水洗浄による水銀回収
方法は、(a)第1に発光管ガラス部材4の含有水銀量
を前記基準値以下のレベルに減少・除去できるほかに、
(b)湿式方式でありながら、前記従来技術での取扱い
注意でコスト高となる希硝酸などの水銀溶解液や硫化物
処理剤等は不要であり、それだけ処理工程及び設備が比
較的簡易に設計できて処理コストを低くできる、(b)
また取扱い注意の水銀溶解液や硫化物処理剤等は不要で
あり、かつ湿式方式ゆえにガラス粉塵などの発生が抑え
られるので、処理工程における作業環境が安全であり、
このように本発明にあたり設定された前記3つの適合条
件を全て満たし得るものである。In the method for recovering mercury by washing with warm water according to the present invention, (a) firstly, in addition to being able to reduce / remove the amount of mercury contained in the arc tube glass member 4 to a level below the reference value,
(B) Although it is a wet method, it does not require a mercury solution such as dilute nitric acid or a sulfide treatment agent, which is expensive due to the handling precautions of the prior art, and the treatment process and equipment are designed relatively simply. And the processing cost can be reduced, (b)
In addition, because mercury-containing liquids and sulfide treatment agents that require careful handling are not necessary, and because the wet method suppresses the generation of glass dust, the working environment in the treatment process is safe,
As described above, all of the three matching conditions set in the present invention can be satisfied.
【0042】一方、上記本実施形態1である図1の使用
済蛍光ランプ1の処理工程及び設備は、本発明の温水洗
浄による水銀回収方法を適用することで基本的な処理コ
ストの低減と作業環境の安全が図られているうえに、更
に循環式の温水循環装置9の導入による節水とエネルギ
ーコスト削減が図られている。また、上記のように温水
洗浄機8に取り付けられた回転撹拌翼12の撹拌効果に
より、洗浄処理時間を約1/3に短縮することができ、
よって洗浄処理工程の高能率化が図られた。On the other hand, the treatment process and equipment of the used fluorescent lamp 1 of FIG. 1 which is the first embodiment is applied with the method for recovering mercury by washing with warm water according to the present invention to reduce the basic treatment cost and work. In addition to environmental safety, the introduction of a circulating hot water circulation device 9 saves water and reduces energy costs. Further, the cleaning effect can be shortened to about 1/3 due to the stirring effect of the rotary stirring blades 12 attached to the hot water washer 8 as described above.
Therefore, the efficiency of the cleaning process was improved.
【0043】本発明者らは、上記本実施形態1である温
水洗浄による水銀回収方法とそれを適用した処理工程及
び設備の効果を再確認するために、実際に図1の処理工
程及び設備を用いて、40Wタイプ使用済蛍光ランプ1
の発光管ガラス部材4のいわゆる実用スケールでの水銀
回収処理を行った。この場合、蛍光体部材5としてハロ
ゲンリン酸蛍光体及び3波長形希土類蛍光体のいずれか
がそれぞれ塗布され、ソーダガラスの発光管ガラス部材
4からなる使用済蛍光ランプ1を用いた。また、直径
1.5m/深長2.0mの円筒形の温水洗浄機8を用いてバ
ッチ当たり4000灯で10バッチの処理を行い、処理
工程条件として温水10の温度50℃で、洗浄処理時間
10分に設定した。この結果、最終のガラスコンテナー
20で回収された発光管ガラス部材4の含有水銀量は
0.0027〜0.0033mg/リットルの範囲に分布し
ており、前記基準値0.005mg/リットル以下のレベ
ルまで確実に減少・除去されていることを確かめた。In order to reconfirm the effect of the method for recovering mercury by the hot water cleaning and the treatment process and equipment to which it is applied, the present inventors actually performed the treatment process and equipment shown in FIG. Use, 40W type used fluorescent lamp 1
The arc glass member 4 was subjected to a so-called practical scale mercury recovery process. In this case, as the phosphor member 5, the used phosphor lamp 1 including the halogen phosphoric acid phosphor and the three-wavelength rare earth phosphor is applied, and the used fluorescent lamp 1 including the soda glass arc tube glass member 4 is used. Also, using a cylindrical hot water washing machine 8 with a diameter of 1.5 m / depth of 2.0 m, 10 batches were processed with 4000 lights per batch, and the treatment process conditions were a temperature of warm water 10 of 50 ° C. and a washing treatment time of 10 Set to minutes. As a result, the amount of mercury contained in the arc tube glass member 4 collected in the final glass container 20 is distributed in the range of 0.0027 to 0.0033 mg / liter, and the level of the standard value of 0.005 mg / liter or less. It was confirmed that it was surely reduced / removed until.
【0044】(実施の形態2)図3は、基本的に上記本
発明の温水洗浄による水銀回収方法を適用した、本発明
実施形態2である使用済蛍光ランプの発光管ガラス部材
の処理工程及び設備の全体構成を示す。(Embodiment 2) FIG. 3 is a process of treating the arc glass member of a used fluorescent lamp according to Embodiment 2 of the present invention, to which the method for recovering mercury by washing with warm water of the present invention is basically applied. The overall configuration of the equipment is shown.
【0045】本実施形態2である発光管ガラス部材10
4の具体的な一連の処理工程及び設備のうちで温水洗浄
による水銀回収以外のものは、前記実施形態1と同様で
ある。そして、本実施形態2である水銀回収の処理工程
及び設備が前記実施形態1と異なる点は、第1に前記実
施形態1でのバッチ処理方式に比べて高能率処理が得ら
れるいわゆる連続処理方式を採用したことである。具体
的に説明すると、まず温水洗浄機108には貯槽109
が付設され、これにより温度制御された所定量の温水が
温水循環ポンプ121、温水循環ライン110を通じて
上側の給水シャワー管111から連続して注入される。
また、温水洗浄機108にはモーター回転される回転ス
クリュー112が取り付けられ、これにより温水洗浄機
108内に連続して投入される発光管ガラス部材104
が、その含有水銀の回収・除去のために回転・撹拌され
ながら規定の処理時間を掛けて洗浄処理されて、その取
出口114を経て最終的に搬送コンベアー117へと連
続して移送されていく。一方、前記給水シャワー管11
1から連続して注入された所定量の温水は、発光管ガラ
ス部材104の水銀回収・除去のための洗浄処理に使用
され、そのうち同じ所定量の温水が排水口115を経て
前記温水循環装置109内に一旦回収・処理されて、こ
れが再び温度制御された温水として給水シャワー管11
1へと供給される。ここで、貯槽109に一旦回収され
た温水に含まれている水銀は、前記実施形態1のときと
同様に貯槽109の底部に蛍光体及びガラス粉体ととも
に沈積し、パンケーキ状の汚泥物116として回収され
る。そして、これが産業廃棄物として無害化処理される
か特別に管理された埋立地へ搬送・処理される。Arc tube glass member 10 according to the second embodiment.
Among the specific series of treatment steps and equipment of 4, except for mercury recovery by washing with warm water, the same as in Embodiment 1 above. The mercury recovery treatment process and equipment according to the second embodiment are different from those of the first embodiment. Firstly, a so-called continuous treatment method capable of obtaining high efficiency treatment as compared with the batch treatment method of the first embodiment. Is adopted. Specifically, first, the hot water washing machine 108 has a storage tank 109.
A predetermined amount of warm water whose temperature is controlled by this is continuously injected from the upper water supply shower pipe 111 through the warm water circulation pump 121 and the warm water circulation line 110.
Further, a rotating screw 112, which is rotated by a motor, is attached to the warm water washing machine 108, whereby the arc tube glass member 104 continuously charged into the warm water washing machine 108.
Is subjected to a cleaning treatment for a prescribed processing time while being rotated and stirred for the recovery and removal of the contained mercury, and is continuously transferred to the conveyor 117 through the outlet 114. . On the other hand, the water supply shower pipe 11
A predetermined amount of hot water continuously injected from 1 is used for cleaning treatment of the arc tube glass member 104 for recovering and removing mercury, and the same predetermined amount of hot water passes through the drain port 115 and the hot water circulating device 109. It is once collected and processed in the water supply shower pipe 11 as hot water whose temperature is controlled again.
1 is supplied. Here, the mercury contained in the hot water once collected in the storage tank 109 is deposited together with the phosphor and the glass powder on the bottom of the storage tank 109 as in the case of the first embodiment, and the pancake-like sludge 116 is obtained. Will be collected as. Then, this is detoxified as industrial waste or transported / treated to a specially managed landfill.
【0046】上記実施形態2である処理工程及び設備の
第1の特徴は、上記のように連続処理方式を採用したこ
とであり、これにより基本的に高能率の処理工程が得ら
れた。もう1つの特徴は、温水洗浄機108に回転スク
リュー112を取り付けたことである。つまり、この回
転・撹拌効果により、連続処理方式でありながら工程処
理条件として温水100の温度を前記実施形態1と同じ
範囲に規定したとき、一方の洗浄処理時間(発光管ガラ
ス部材104が温水洗浄機108に投入されて搬送コン
ベアー117に移送されるまでの時間)を前記実施形態
1と同じ範囲まで短縮・規定することができた。The first feature of the treatment process and equipment according to the second embodiment is that the continuous treatment system is adopted as described above, and thereby a treatment process of high efficiency is basically obtained. Another feature is that the rotary screw 112 is attached to the hot water washing machine 108. In other words, due to this rotation / stirring effect, when the temperature of the hot water 100 is defined as the same range as in the first embodiment as a process treatment condition even though it is a continuous treatment system, one cleaning treatment time (the arc tube glass member 104 is washed with warm water It was possible to shorten / define the time period from the time when the machine was loaded into the machine 108 to the time when it was transferred to the conveyor 117) within the same range as in the first embodiment.
【0047】本発明者らは、前記実施形態1の場合と同
様に、実際に図3の処理工程及び設備を用いて、前記と
同じ40Wタイプ使用済蛍光ランプ101の発光管ガラ
ス部材104の実用スケールでの水銀回収処理を行なっ
た。この場合、直径1.0m/全長5.0mの円筒形の温水
洗浄機108を用いて、処理工程条件として温水の温度
50℃で洗浄処理時間10分に設定し、時間当たり20
00灯の処理を連続48hrs行なった。この結果、最終
のガラスコンテナー120で回収された発光管ガラス部
材104の含有水銀量は0.0026〜0.0035mg/
リットルの範囲に分布しており、前記基準値0.005m
g/リットル以下のレベルまで確実に減少・除去されて
いることを確かめた。As in the case of the first embodiment, the present inventors actually used the processing steps and equipment of FIG. 3 to put the arc tube glass member 104 of the same 40 W type used fluorescent lamp 101 into practical use. A mercury recovery process on a scale was performed. In this case, using a cylindrical hot water washing machine 108 having a diameter of 1.0 m / total length of 5.0 m, the washing process time is set to 10 minutes at a hot water temperature of 50 ° C. as a treatment process condition, and the washing treatment time is 20 minutes per hour.
The treatment of 00 lights was continuously performed for 48 hours. As a result, the amount of mercury contained in the arc tube glass member 104 recovered in the final glass container 120 is 0.0026 to 0.0035 mg /
It is distributed in the range of liters and the standard value is 0.005m.
It was confirmed that it was surely reduced / removed to the level of g / liter or less.
【0048】(実施の形態3)図4は、基本的に上記本
発明の温水洗浄による水銀回収方法を適用した、本発明
実施形態3である使用済蛍光ランプの発光管ガラス部材
の処理工程及び設備の全体構成を示す。(Embodiment 3) FIG. 4 is a treatment process of an arc tube glass member of a used fluorescent lamp according to Embodiment 3 of the present invention, to which the method for recovering mercury by washing with warm water according to the present invention is basically applied. The overall configuration of the equipment is shown.
【0049】本実施形態3である発光管ガラス部材20
4の具体的な一連の処理工程及び設備のうちで温水洗浄
による水銀回収以外のものは、前記実施形態2と同様で
ある。そして、本実施形態3である水銀回収の処理工程
及び設備が前記実施形態2と異なる点は、基本的には同
じ連続処理方式を採用しているが、特有の構成からなる
温水洗浄機208を採用したことである。具体的には、
円筒形の温水洗浄機208はそれ自体がモーター回転さ
れるという特有の構成からなり、これにより温水洗浄機
208内に連続して投入される発光管ガラス部材204
が、その含有水銀の回収・除去のために回転・撹拌され
ながら規定の処理時間を掛けて洗浄処理されて、その取
出口214を経て最終的に搬送コンベアー217へと連
続して移送されていく。なお、温水洗浄機208に付設
された貯槽209及び給水シャワー管211の構成及び
機能・動作は、前記実施形態2と同様である。Arc tube glass member 20 according to the third embodiment.
Of the specific series of treatment steps and equipment of No. 4, except for mercury recovery by washing with warm water, it is the same as in the second embodiment. The third embodiment is different from the second embodiment in the mercury recovery treatment process and equipment, but basically the same continuous treatment system is adopted, but a warm water washing machine 208 having a unique configuration is used. It is adopted. In particular,
The cylindrical hot water washer 208 has a unique structure in which the motor is rotated by itself, so that the arc tube glass member 204 continuously charged into the hot water washer 208.
Is subjected to a cleaning treatment for a prescribed processing time while being rotated and stirred for the recovery and removal of the contained mercury, and is finally continuously transferred to the transfer conveyor 217 via the outlet 214. . The configurations, functions, and operations of the storage tank 209 and the water supply shower pipe 211 attached to the warm water washing machine 208 are the same as those in the second embodiment.
【0050】上記実施形態3である処理工程及び設備の
特徴は、上記のようにそれ自体がモーター回転されると
いう特有の構成からなる温水洗浄機208を採用したこ
とである。この回転・撹拌効果により、前記実施形態2
の場合と全く同様に、連続処理方式でありながら工程処
理条件として温水の温度を前記実施形態1と同じ範囲に
規定したとき、一方の洗浄処理時間を前記実施形態1と
同じ範囲まで短縮・規定することができた。A feature of the treatment process and equipment according to the third embodiment is that the warm water washing machine 208 having a peculiar structure in which the motor itself is rotated as described above is adopted. Due to this rotation / stirring effect, the second embodiment
In the same manner as in the above case, when the temperature of hot water is defined as the same range as in the first embodiment as the process treatment condition in spite of the continuous treatment method, one cleaning treatment time is shortened / specified to the same range as in the first embodiment. We were able to.
【0051】本発明者は、前記実施形態2の場合と同様
に、実際に図4の処理工程及び設備を用いて、前記と同
じ40Wタイプ使用済蛍光ランプ201の発光管ガラス
部材204の実用スケールでの水銀回収処理を行なっ
た。この場合、直径1.0m/全長5.0mの円筒形の温水
洗浄機208を用いて、処理工程条件として温水の温度
50℃で洗浄処理時間10分に設定し、時間当たり20
00灯の処理を連続48hrs行なった。この結果、最終
のガラスコンテナー220で回収された発光管ガラス部
材204の含有水銀量は0.0026〜0.0036mg/
リットルの範囲に分布しており、前記基準値0.005m
g/リットル以下のレベルまで確実に減少・除去されて
いることを確かめた。As in the case of the second embodiment, the inventor of the present invention actually uses the processing steps and equipment of FIG. 4 to make a practical scale of the arc tube glass member 204 of the same 40 W type used fluorescent lamp 201 as described above. The mercury recovery process was performed. In this case, by using a cylindrical hot water washing machine 208 having a diameter of 1.0 m / total length of 5.0 m, the washing process time is set to 10 minutes at a hot water temperature of 50 ° C. as a treatment process condition, and the washing treatment time is 20 minutes per hour.
The treatment of 00 lights was continuously performed for 48 hours. As a result, the amount of mercury contained in the arc tube glass member 204 recovered in the final glass container 220 is 0.0026 to 0.0036 mg /
It is distributed in the range of liters and the standard value is 0.005m.
It was confirmed that it was surely reduced / removed to the level of g / liter or less.
【0052】なお、上記本実施形態で示された温水洗浄
による水銀回収方法とそれを適用した処理工程及び設備
は、発光管ガラス部材としてソーダガラスに代ってナト
リウムフリーのバリウム系ガラス等を用いた使用済蛍光
ランプの水銀回収処理にも適用できるものである。The method of recovering mercury by washing with hot water and the treatment process and equipment to which the method is applied in the above-described embodiment uses sodium-free barium-based glass or the like as the arc glass member instead of soda glass. It can also be applied to the mercury recovery process of used fluorescent lamps.
【0053】以上のように、廃蛍光ランプ、特に使用済
蛍光ランプの発光管ガラス部材の水銀回収処理におい
て、上記本実施形態で示された温水洗浄を特徴とする水
銀回収方法を適用することにより、発光管ガラス部材の
含有水銀量を前記基準値0.005mg/リットル以下の
レベルまで除去でき、かつ低処理コストで安全な作業環
境からなる水銀回収の処理方法及び装置が具現できる。As described above, in the mercury recovery processing of the arc tube glass member of the waste fluorescent lamp, particularly the used fluorescent lamp, by applying the mercury recovery method characterized by the warm water washing shown in the above-mentioned embodiment. In addition, it is possible to realize a mercury recovery treatment method and apparatus which can remove the mercury content of the arc tube glass member to a level of the above-mentioned standard value of 0.005 mg / liter or less and which has a low treatment cost and a safe working environment.
【0054】[0054]
【発明の効果】本発明によれば、廃蛍光ランプ、特に使
用済蛍光ランプの発光管ガラス部材の水銀回収処理にお
いて、前記発光管ガラス部材の含有水銀量を規定基準値
0.005mg/リットル以下のレベルまで回収・除去で
き、かつ低処理コストで作業環境も安全な水銀回収方法
が得られて、これを基本的に適用することにより前記発
光管ガラス部材のリサイクル使用を進捗するような処理
方法及び装置が具現できる。According to the present invention, in the mercury recovery process of the arc tube glass member of a waste fluorescent lamp, particularly a used fluorescent lamp, the mercury content of the arc tube glass member is not more than a specified standard value of 0.005 mg / liter. A method of recovering mercury that can be recovered and removed to the level of, and that has a low processing cost and a safe working environment, and which is basically applied to promote the recycling use of the arc tube glass member And a device can be realized.
【図1】本発明の実施の形態1における使用済蛍光ラン
プの水銀回収方法と装置の構成図FIG. 1 is a configuration diagram of a mercury recovery method and device for a used fluorescent lamp according to a first embodiment of the present invention.
【図2】本発明の実施の形態1における温水洗浄処理に
おける温水温度と含有水銀量の減少割合の関係を示すグ
ラフFIG. 2 is a graph showing the relationship between the temperature of hot water and the rate of decrease in the amount of contained mercury in the hot water cleaning process in the first embodiment of the present invention.
【図3】本発明の実施の形態2における使用済蛍光ラン
プの処理工程及び装置の構成図FIG. 3 is a configuration diagram of a processing step and an apparatus of a used fluorescent lamp according to a second embodiment of the present invention.
【図4】本発明の実施の形態3における使用済蛍光ラン
プの処理工程及び装置の構成図FIG. 4 is a configuration diagram of a processing step and an apparatus of a used fluorescent lamp according to a third embodiment of the present invention.
1,101,201 使用済蛍光ランプ
2,3,102,103,202,203 口金付ステ
ムガラス部材
4,104,204 発光管ガラス部材
5,105,205 蛍光体部材
6,106,206 破砕機
7,17,107,117,207,217 搬送コン
ベアー
8,108,208 温水洗浄機
9,109,209 貯槽
10,110,210 温水循環ライン
11,111,211 給水(シャワー)管
12,112 撹拌翼(スクリュー)
16,116,216 水銀含有の汚泥物
18,118,218 ロータリー乾燥機
19,119,219 温風循環装置
20,120,220 ガラスコンテナー
21,121,221 温水循環ポンプ1, 101, 201 Used fluorescent lamps 2, 3, 102, 103, 202, 203 Stem glass member with base 4, 104, 204 Arc tube glass member 5, 105, 205 Fluorescent material member 6, 106, 206 Crusher 7 , 17, 107, 117, 207, 217 Conveyors 8, 108, 208 Hot water washer 9, 109, 209 Storage tanks 10, 110, 210 Hot water circulation line 11, 111, 211 Water (shower) pipe 12, 112 Stirrer blade ( Screw) 16,116,216 Sludge containing mercury 18,118,218 Rotary dryer 19,119,219 Hot air circulation device 20,120,220 Glass container 21,121,221 Hot water circulation pump
───────────────────────────────────────────────────── フロントページの続き (72)発明者 藤浪 清勝 大阪府門真市大字門真1006番地 松下電器 産業株式会社内 (72)発明者 笹田 壽一 大阪府門真市大字門真1006番地 松下電器 産業株式会社内 Fターム(参考) 4D004 AA50 AB03 BA02 BA05 BA06 CA04 CA13 CA15 CA22 CA40 CA42 CB36 CB45 CB50 DA03 DA06 ─────────────────────────────────────────────────── ─── Continued front page (72) Inventor Kiyokatsu Fujinami 1006 Kadoma, Kadoma-shi, Osaka Matsushita Electric Sangyo Co., Ltd. (72) Inventor Toshikazu Sasada 1006 Kadoma, Kadoma-shi, Osaka Matsushita Electric Sangyo Co., Ltd. F-term (reference) 4D004 AA50 AB03 BA02 BA05 BA06 CA04 CA13 CA15 CA22 CA40 CA42 CB36 CB45 CB50 DA03 DA06
Claims (6)
ス部材から水銀を回収する方法であって、 前記発光管ガラス部材を破砕し、 前記破砕物を温水洗浄機に投入して温水とともに攪拌
し、ガラス破砕物と水銀に分離し、 前記分離された水銀は温水とともに貯槽に入れ、前記貯
槽の下部に沈殿させて回収し、 前記ガラス破砕物は乾燥して取り出し、 前記貯槽の上澄み液の温水はリサイクルして温水洗浄機
に供給することを特徴とする廃蛍光ランプの水銀回収方
法。1. A method for recovering mercury from an arc tube glass member separated from a waste fluorescent lamp, wherein the arc tube glass member is crushed, and the crushed material is put into a hot water washing machine and stirred with hot water. , Glass crushed material and mercury are separated, the separated mercury is put in a storage tank together with warm water, precipitated and collected at the bottom of the storage tank, the glass crushed material is dried and taken out, and hot water of the supernatant liquid of the storage tank Is a method of recovering mercury from waste fluorescent lamps, which is recycled and supplied to a hot water washer.
度が、35℃以上の範囲である請求項1に記載の廃蛍光
ランプの水銀回収方法。2. The method for recovering mercury from a waste fluorescent lamp according to claim 1, wherein the temperature of the hot water used in the hot water washing treatment is in the range of 35 ° C. or higher.
度が、80℃以下の範囲である請求項1または2に記載
の廃蛍光ランプの水銀回収方法。3. The method for recovering mercury from a waste fluorescent lamp according to claim 1, wherein the temperature of the hot water used for the hot water washing treatment is in the range of 80 ° C. or lower.
ス部材から水銀を回収する装置であって、 前記発光管ガラス部材を破砕する手段と、 前記破砕物を温水洗浄機に投入する手段と、前記温水洗
浄機に温水を供給する手段と、ガラス破砕物と水銀に分
離するための攪拌手段とを備え、 前記分離された水銀を温水とともに貯槽に入れ、前記貯
槽の下部に沈殿させて回収する手段と、 前記ガラス破砕物を乾燥して取り出す手段と、 前記貯槽の上澄み液の温水はリサイクルして温水洗浄機
に供給する手段を備えたことを特徴とする廃蛍光ランプ
の水銀回収装置。4. An apparatus for recovering mercury from an arc tube glass member separated from a waste fluorescent lamp, said means for crushing said arc tube glass member, and means for charging said crushed material into a hot water washer. A means for supplying hot water to the hot water washing machine and a stirring means for separating glass crushed material and mercury are provided, and the separated mercury is put into a storage tank together with the hot water, and is precipitated and collected in the lower part of the storage tank. A mercury recovery device for a waste fluorescent lamp, comprising: means, means for drying and taking out the crushed glass, and means for recycling hot water of the supernatant liquid of the storage tank and supplying it to a hot water washing machine.
が、バッチ式または連続式である請求項4に記載の廃蛍
光ランプの水銀回収装置。5. The mercury recovery apparatus for a waste fluorescent lamp according to claim 4, wherein the treatment in the hot water washer with an agitator is a batch type or a continuous type.
拌機による攪拌または前記温水洗浄機の槽が回転するこ
とによる攪拌である請求項4または5に記載の廃蛍光ラ
ンプの水銀回収装置。6. The mercury recovery apparatus for a waste fluorescent lamp according to claim 4, wherein the stirring means in the hot water washing machine is stirring by a stirring machine or by rotating a tank of the hot water washing machine.
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JP2001367277A JP3669956B2 (en) | 2001-11-30 | 2001-11-30 | Mercury recovery method and equipment for waste fluorescent lamps |
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Cited By (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
KR20050069365A (en) * | 2003-12-31 | 2005-07-05 | 삼성전자주식회사 | Method of recycling fluorescent lamp and recycling apparatus using the same |
JP2008307439A (en) * | 2007-06-12 | 2008-12-25 | Sawaya:Kk | Method for disposing of low-pressure sodium lamp and its disposer |
JP2010042346A (en) * | 2008-08-12 | 2010-02-25 | Jfe Mineral Co Ltd | Pretreatment method for recovering rare earth element from disposed fluorescent lamp and method of recovering rare earth element using solid matter obtained by the pretreatment method |
JP2010172812A (en) * | 2009-01-28 | 2010-08-12 | Sanyo Special Steel Co Ltd | Method for decreasing elution amount of heavy metal of steelmaking dust |
WO2013127245A1 (en) * | 2012-03-01 | 2013-09-06 | 深圳市格林美高新技术股份有限公司 | Recycling apparatus for waste lamp tubes |
-
2001
- 2001-11-30 JP JP2001367277A patent/JP3669956B2/en not_active Expired - Fee Related
Cited By (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
KR20050069365A (en) * | 2003-12-31 | 2005-07-05 | 삼성전자주식회사 | Method of recycling fluorescent lamp and recycling apparatus using the same |
JP2008307439A (en) * | 2007-06-12 | 2008-12-25 | Sawaya:Kk | Method for disposing of low-pressure sodium lamp and its disposer |
JP2010042346A (en) * | 2008-08-12 | 2010-02-25 | Jfe Mineral Co Ltd | Pretreatment method for recovering rare earth element from disposed fluorescent lamp and method of recovering rare earth element using solid matter obtained by the pretreatment method |
JP2010172812A (en) * | 2009-01-28 | 2010-08-12 | Sanyo Special Steel Co Ltd | Method for decreasing elution amount of heavy metal of steelmaking dust |
WO2013127245A1 (en) * | 2012-03-01 | 2013-09-06 | 深圳市格林美高新技术股份有限公司 | Recycling apparatus for waste lamp tubes |
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