JP7392913B2 - Demineralization cleaning method for chlorine-containing ash - Google Patents
Demineralization cleaning method for chlorine-containing ash Download PDFInfo
- Publication number
- JP7392913B2 JP7392913B2 JP2020032490A JP2020032490A JP7392913B2 JP 7392913 B2 JP7392913 B2 JP 7392913B2 JP 2020032490 A JP2020032490 A JP 2020032490A JP 2020032490 A JP2020032490 A JP 2020032490A JP 7392913 B2 JP7392913 B2 JP 7392913B2
- Authority
- JP
- Japan
- Prior art keywords
- slurry
- chlorine
- ash
- less
- cleaning
- 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.)
- Active
Links
- ZAMOUSCENKQFHK-UHFFFAOYSA-N Chlorine atom Chemical compound [Cl] ZAMOUSCENKQFHK-UHFFFAOYSA-N 0.000 title claims description 40
- 229910052801 chlorine Inorganic materials 0.000 title claims description 40
- 239000000460 chlorine Substances 0.000 title claims description 40
- 238000000034 method Methods 0.000 title claims description 37
- 238000004140 cleaning Methods 0.000 title claims description 33
- 238000005115 demineralization Methods 0.000 title description 2
- 230000002328 demineralizing effect Effects 0.000 title description 2
- 239000002002 slurry Substances 0.000 claims description 87
- 239000002245 particle Substances 0.000 claims description 33
- 239000010419 fine particle Substances 0.000 claims description 31
- 238000003756 stirring Methods 0.000 claims description 30
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 20
- 238000010612 desalination reaction Methods 0.000 claims description 18
- 230000018044 dehydration Effects 0.000 claims description 9
- 238000006297 dehydration reaction Methods 0.000 claims description 9
- 238000011033 desalting Methods 0.000 claims description 8
- 230000003068 static effect Effects 0.000 claims description 6
- 229920000642 polymer Polymers 0.000 claims description 5
- 239000002956 ash Substances 0.000 description 57
- 238000001914 filtration Methods 0.000 description 36
- 239000010802 sludge Substances 0.000 description 7
- 238000004062 sedimentation Methods 0.000 description 6
- 238000005406 washing Methods 0.000 description 5
- 239000010881 fly ash Substances 0.000 description 3
- 239000013049 sediment Substances 0.000 description 3
- 239000007787 solid Substances 0.000 description 3
- QAOWNCQODCNURD-UHFFFAOYSA-N Sulfuric acid Chemical compound OS(O)(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-N 0.000 description 2
- 239000004568 cement Substances 0.000 description 2
- 239000000428 dust Substances 0.000 description 2
- 238000002156 mixing Methods 0.000 description 2
- 239000000843 powder Substances 0.000 description 2
- 238000010298 pulverizing process Methods 0.000 description 2
- 239000000126 substance Substances 0.000 description 2
- 239000006228 supernatant Substances 0.000 description 2
- 238000013019 agitation Methods 0.000 description 1
- 150000001805 chlorine compounds Chemical class 0.000 description 1
- 239000011362 coarse particle Substances 0.000 description 1
- 239000011248 coating agent Substances 0.000 description 1
- 238000000576 coating method Methods 0.000 description 1
- 238000010586 diagram Methods 0.000 description 1
- 230000000694 effects Effects 0.000 description 1
- 238000005469 granulation Methods 0.000 description 1
- 230000003179 granulation Effects 0.000 description 1
- 239000003002 pH adjusting agent Substances 0.000 description 1
- 239000002994 raw material Substances 0.000 description 1
- -1 stirred and washed Substances 0.000 description 1
- 239000002351 wastewater Substances 0.000 description 1
Images
Landscapes
- Processing Of Solid Wastes (AREA)
Description
本発明は、塩素含有灰をスラリーにして脱塩洗浄する際に、スラリー中の灰を過粉砕することなく粒度分布を制御することによって、濾過性に優れた灰スラリーにして連続ろ過を可能にした脱塩洗浄方法に関する。 The present invention enables continuous filtration of ash slurry with excellent filterability by controlling the particle size distribution without over-pulverizing the ash in the slurry when turning chlorine-containing ash into a slurry for desalination washing. The present invention relates to a demineralization cleaning method.
飛灰や塩素バイパスダストなどの塩素含有灰は、脱塩することによってセメントの原料に利用される。塩素化合物は大部分が水溶性であるため、塩素含有灰の脱塩方法として水洗が用いられる場合が多い。具体的には、塩素含有灰を撹拌洗浄槽に入れて水スラリーにし、撹拌洗浄して塩素分を溶出させたスラリーを濾過し脱水して塩素分を含む水を除去することによって脱塩している。 Chlorine-containing ash, such as fly ash and chlorine bypass dust, can be desalinated and used as a raw material for cement. Since most chlorine compounds are water-soluble, washing with water is often used as a method for desalting chlorine-containing ash. Specifically, chlorine-containing ash is put into a stirring cleaning tank to make a water slurry, and the slurry, which has been stirred and washed to elute the chlorine content, is filtered and dehydrated to remove the chlorine-containing water. There is.
上記スラリーの濾過処理において、スラリーの固体濃度が希薄であるほど濾過性が低下するので、従来の脱塩システムでは、撹拌洗浄槽の次に沈降槽を設け、撹拌洗浄後のスラリーを沈降槽に導き、ここでスラリー中の灰を沈降させて上澄み水を除去し、スラリーを濃縮した後に、濾過工程に送る構成を採用している。 In the above slurry filtration process, the thinner the solid concentration of the slurry, the lower the filterability, so in conventional desalination systems, a settling tank is installed next to the stirring washing tank, and the slurry after stirring and washing is transferred to the settling tank. The system employs a structure in which the ash in the slurry is allowed to settle, the supernatant water is removed, and the slurry is concentrated before being sent to the filtration process.
しかし、従来の上記脱塩システムでは、撹拌洗浄槽でスラリーを撹拌し続けるためにスラリー中の灰が過粉砕され、粒径0.045mm未満の微粒子の割合が多い。このような微粒子は水切れが悪く、しかも沈降槽に長時間静置されることによって層状の堆積層を形成し、濾過性をさらに低下させている。 However, in the above-mentioned conventional desalting system, the ash in the slurry is over-pulverized because the slurry is continuously stirred in the stirring cleaning tank, and the proportion of fine particles with a particle size of less than 0.045 mm is high. Such fine particles are difficult to drain, and when left standing in a sedimentation tank for a long time, they form a layered sedimentary layer, further reducing filterability.
洗浄スラリーの濾過性を改善するため次のような方法が知られている。(イ)加圧粒状化してから濾過する方法(特許文献1)、(ロ)比較的粗粒な灰のスラリーでベルトフィルター表面をプレコートしてから微粒灰スラリーを濾過する方法(特許文献2)、(ハ)洗浄スラリーに高分子凝集剤を加えて凝集フロックを沈降分離させて初期濃縮スラリーを形成し、該初期濃縮スラリーを加水した後に湿式サイクロンを用いて細粒スラリーと粗粒スラリーに分離し、該細粒スラリーに高分子凝集剤を加えて細粒凝集フロックを沈降 分離させて細粒濃縮スラリーを形成し、該細粒濃縮スラリーを脱水洗浄して脱塩する方法(特許文献3)、(ニ)洗浄灰と粗粒な無機粉体を混合して粒度調整する方法(特許文献4)、(ホ)薬剤を添加してスラリーの粘性増加を抑制し、スラリーの流動性と脱水性を高める方法(特許文献5)。また、(ヘ)焼却灰に含まれる塩素は細粒物に多いことから、粒径0.5mm未満の細粒子と粒径0.5mm以上の粗粒子に篩分けして脱塩処理する方法が知られている(特許文献6)。 The following methods are known to improve the filterability of cleaning slurry. (a) A method of pressurizing granulation and then filtering (Patent Document 1), (b) A method of pre-coating the surface of the belt filter with relatively coarse ash slurry and then filtering the fine ash slurry (Patent Document 2) (c) Add a polymer flocculant to the washed slurry to sediment and separate the flocs to form an initial concentrated slurry, and after adding water to the initial concentrated slurry, separate it into a fine slurry and a coarse slurry using a wet cyclone. A method in which a polymer flocculant is added to the fine particle slurry to sediment and separate the fine particle flocs to form a fine particle concentrated slurry, and the fine particle concentrated slurry is dehydrated and washed to desalinate (Patent Document 3) , (d) A method of adjusting the particle size by mixing washed ash and coarse inorganic powder (Patent Document 4), (e) Adding a chemical to suppress the increase in viscosity of the slurry, improving the fluidity and dewatering properties of the slurry. (Patent Document 5). In addition, (f) Since the chlorine contained in incinerated ash is mostly found in fine particles, it is recommended to sieve it into fine particles with a particle size of less than 0.5 mm and coarse particles with a particle size of 0.5 mm or more for desalination treatment. known (Patent Document 6).
上記(イ)(ロ)の方法は装置の改良が大がかりになるとともに、飛灰によって性状が大きく異なるので十分な効果が得られない場合がある。上記(ハ)の方法は設備が大がかりであり、上記(ニ)の方法は無機粉体を混合することによって見かけ上の粒度は調整されるが、微細な灰は残るので濾過性は根本的には解決されない。上記(ホ)の方法は薬剤添加によって濾過性はある程度改善されるが、根本的な解決にはならない。また上記(ヘ)の方法は、濾過性は殆ど改善されない。 Methods (a) and (b) above require extensive equipment improvements, and the properties of fly ash vary greatly, so sufficient effects may not be obtained. The method (c) above requires large-scale equipment, and the method (d) above adjusts the apparent particle size by mixing inorganic powder, but since fine ash remains, the filtration performance is fundamentally affected. is not resolved. Although the above method (e) improves filtration performance to some extent by adding chemicals, it does not provide a fundamental solution. In addition, the above method (f) hardly improves filtration performance.
本発明は、従来の脱塩処理における上記問題を解決した脱塩洗浄方法を提供するものであり、装置の大掛かりな改良を必要とせず、濾過性に優れた処理能力の高い脱塩洗浄方法を提供する。 The present invention provides a desalination cleaning method that solves the above-mentioned problems in conventional desalination processing, and provides a desalination cleaning method that has excellent filtration performance and high throughput without requiring major improvements in equipment. provide.
本発明は以下の構成によって従来の問題を解決した脱塩洗浄方法に関する。
〔1〕塩素含有灰を水スラリーにして撹拌洗浄し、塩素分が溶出した水を脱水して、塩素を低減した灰を回収する脱塩洗浄方法であって、該スラリーに高分子凝集剤を添加して該スラリー中の粒径0.045mm未満の微粒子の割合が50wt%以下になるように撹拌洗浄し、該撹拌洗浄したスラリーを、静置沈降工程を経ずにベルトフィルターに送って脱水することを特徴とする塩素含有灰の脱塩洗浄方法。
〔2〕上記撹拌洗浄において、上記スラリー中の粒径0.045mm未満の微粒子の割合が10wt%以下になるように撹拌洗浄する上記[1]に記載する塩素含有灰の脱塩洗浄方法。
〔3〕塩素含有灰に3~5倍量の水を加えてスラリーにする上記[1]または上記[2]に記載する塩素含有灰の脱塩洗浄方法。
The present invention relates to a desalination cleaning method that solves the conventional problems with the following configuration.
[1] A desalination cleaning method in which chlorine-containing ash is made into a water slurry, stirred and washed, the water from which the chlorine content has been eluted is dehydrated, and ash with reduced chlorine is recovered. The slurry is stirred and washed so that the proportion of fine particles with a particle size of less than 0.045 mm in the slurry is 50 wt% or less, and the stirred and washed slurry is sent to a belt filter for dehydration without going through a static settling process. A method for desalinating and cleaning chlorine-containing ash, characterized by:
[2] The method for desalting and cleaning chlorine-containing ash described in [1] above, wherein the stirring and cleaning is performed so that the proportion of fine particles with a particle size of less than 0.045 mm in the slurry is 10 wt% or less.
[3] The method for desalinating and cleaning chlorine-containing ash described in [1] or [2] above, in which 3 to 5 times the amount of water is added to the chlorine-containing ash to form a slurry.
〔具体的な説明〕
本発明の脱塩洗浄方法は、塩素含有灰を水スラリーにして撹拌洗浄し、塩素分が溶出した水を脱水して、塩素を低減した灰を回収する脱塩洗浄方法であって、該スラリーに高分子凝集剤を添加して該スラリー中の粒径0.045mm未満の微粒子の割合が50wt%以下になるように撹拌洗浄した後に、該撹拌洗浄したスラリーを、静置沈降工程を経ずにベルトフィルターに送って脱水することを特徴とする塩素含有灰の脱塩洗浄方法である。
[Specific explanation]
The desalination cleaning method of the present invention is a desalination cleaning method in which chlorine-containing ash is made into a water slurry, stirred and washed, water in which chlorine content has been eluted is dehydrated, and ash with reduced chlorine is recovered, and the slurry is After adding a polymer flocculant to the slurry and stirring and cleaning it so that the proportion of fine particles with a particle size of less than 0.045 mm in the slurry is 50 wt% or less, the stirring and cleaning slurry is stirred and washed without going through a static settling process. This is a desalination cleaning method for chlorine-containing ash, which is characterized by sending it to a belt filter for dehydration.
上記塩素含有灰のスラリー(以下、塩素含有灰スラリーと云う)は、例えば、飛灰やセメント工場の塩素バイパスダストなどから回収される塩素含有灰を水に分散してpH6~10前後に調整したスラリーである。pH調整剤として硫酸が添加されたスラリーや、脱塩処理後の廃水汚泥を塩素含有灰と共にスラリーにしたものなども、本発明の塩素含有灰スラリーに含まれる。 The above slurry of chlorine-containing ash (hereinafter referred to as chlorine-containing ash slurry) is prepared by dispersing chlorine-containing ash recovered from fly ash or chlorine bypass dust of a cement factory in water and adjusting the pH to around 6 to 10. It is slurry. The chlorine-containing ash slurry of the present invention also includes a slurry to which sulfuric acid is added as a pH adjuster, and a slurry made from desalinated wastewater sludge together with chlorine-containing ash.
本発明の脱塩洗浄方法は、上記塩素含有灰スラリーを撹拌槽で撹拌洗浄する際に、スラリー中の粒径0.045mm未満の微粒子の割合が50wt%以下になるように撹拌洗浄する。撹拌洗浄した上記スラリーを濾過脱水するときに、脱水完了までの濾過時間は該スラリーに含まれる粒径0.045mm未満の微粒子の割合によって大きく異なることが見出された。 In the desalination cleaning method of the present invention, when the chlorine-containing ash slurry is stirred and washed in a stirring tank, the slurry is stirred and washed so that the proportion of fine particles with a particle size of less than 0.045 mm in the slurry is 50 wt% or less. It has been found that when the slurry that has been stirred and washed is filtered and dehydrated, the filtration time until the dehydration is completed varies greatly depending on the proportion of fine particles with a particle size of less than 0.045 mm contained in the slurry.
図1に示す例では、灰Aについて、スラリーに含まれる粒径0.045mm未満の微粒子の割合が(イ)2wt%未満、(ロ)50wt%、(ハ)100wt%であるときの濾過時間は、(イ)は13秒、(ロ)は335秒、(ハ)は823秒であり、スラリーに含まれる粒径0.045mm未満の微粒子の割合によって濾過時間が大幅に異なる。 In the example shown in Fig. 1, for ash A, the filtration time when the proportion of fine particles with a particle size of less than 0.045 mm contained in the slurry is (a) less than 2wt%, (b) 50wt%, and (c) 100wt%. (A) is 13 seconds, (B) is 335 seconds, and (C) is 823 seconds, and the filtration time varies greatly depending on the proportion of fine particles with a particle size of less than 0.045 mm contained in the slurry.
スラリーに含まれる粒径0.045mm未満の微粒子の割合はスラリーの撹拌時間に依存している。図2に示す例では、灰Aについて、粒径0.045mm未満の微粒子の割合は、300分の撹拌時間では12wt%であり、15分の撹拌時間では6wt%である。また、灰Bについては、粒径0.045mm未満の微粒子の割合は、300分の撹拌時間では27wt%であり、15分の撹拌時間では2wt%である。 The proportion of fine particles with a particle size of less than 0.045 mm contained in the slurry depends on the stirring time of the slurry. In the example shown in FIG. 2, for ash A, the proportion of fine particles with a particle size of less than 0.045 mm is 12 wt% at a stirring time of 300 minutes, and 6 wt% at a stirring time of 15 minutes. Regarding ash B, the proportion of fine particles with a particle size of less than 0.045 mm is 27 wt% when the stirring time is 300 minutes, and 2 wt% when the stirring time is 15 minutes.
本発明は、上記知見に基づき、塩素含有灰スラリーの撹拌洗浄において、スラリー中の粒径0.045mm未満の微粒子の割合が50wt%以下、好ましくは10wt%以下になるように撹拌時間を制御する。撹拌時間が長すぎると過粉砕になり、0.045mm未満の微粒子の割合が増加する。この撹拌時間および撹拌速度などは撹拌洗浄槽の仕様に従って定めればよい。 Based on the above findings, the present invention, in stirring and cleaning chlorine-containing ash slurry, controls the stirring time so that the proportion of fine particles with a particle size of less than 0.045 mm in the slurry is 50 wt% or less, preferably 10 wt% or less. . If the stirring time is too long, over-pulverization will occur and the proportion of fine particles less than 0.045 mm will increase. The stirring time, stirring speed, etc. may be determined according to the specifications of the stirring cleaning tank.
図1に示すように、粒径0.045mm未満の微粒子の割合が少ないほど濾過時間は短縮されるので、スラリー中の粒径0.045mm未満の微粒子の割合は50wt%以下が好ましく、10wt%以下がより好ましい。 As shown in Figure 1, the smaller the proportion of fine particles with a particle size of less than 0.045 mm, the shorter the filtration time, so the proportion of fine particles with a particle size of less than 0.045 mm in the slurry is preferably 50 wt% or less, and 10 wt%. The following are more preferable.
また、撹拌洗浄の際に、高分子凝集剤を添加することによって微細粒子が凝集して粒径0.045mm以上の粒子になりやすいので、粒径0.045mm未満の微粒子の割合を抑制することができる。 In addition, during agitation cleaning, adding a polymer flocculant tends to cause fine particles to coagulate into particles with a particle size of 0.045 mm or more, so the proportion of fine particles with a particle size of less than 0.045 mm should be suppressed. I can do it.
本発明の脱塩洗浄方法では、上記撹拌洗浄した後に、該撹拌洗浄したスラリーを、静置沈降工程を経ずにベルトフィルターに送って脱水する。従来の脱塩設備は、塩素含有灰スラリーの撹拌洗浄槽と沈降槽を有しており、撹拌洗浄した塩素含有灰スラリーを沈降槽に導いて該沈降槽でスラリーを静置して沈降させ、上澄み水を除去し、堆積したスラリー汚泥をベルトフィルターに送り、移送しながら脱水している。 In the desalting and cleaning method of the present invention, after the above-mentioned stirring and cleaning, the slurry that has been stirred and cleaned is sent to a belt filter for dehydration without going through a stationary sedimentation step. Conventional desalination equipment has a stirring cleaning tank and a settling tank for the chlorine-containing ash slurry, and leads the stirred and washed chlorine-containing ash slurry to the settling tank, and allows the slurry to settle in the settling tank, The supernatant water is removed, and the accumulated slurry sludge is sent to a belt filter, where it is dehydrated while being transported.
ここで、静置沈降処理と濾過処理の関係を検討すると、静置時間によって濾過時間が異なり、静置時間に比例して濾過時間が長くなることが見出された。図3に示すように、スラリーを静置せずに濾過した場合(静置0時間)と、72時間静置して濾過した場合を比較すると、灰Aについて、静置しないときの濾過時間は12秒であるが、72時間静置した後の濾過時間は22秒である。また灰Bについて、静置しないときの濾過時間は7秒であるが、72時間静置後の濾過時間は10秒であり、灰Aおよび灰Bの何れの場合も静置後の濾過時間が長くなる。 When examining the relationship between the standing sedimentation treatment and the filtration treatment, it was found that the filtration time differs depending on the standing time, and that the filtration time becomes longer in proportion to the standing time. As shown in Figure 3, when comparing the case where the slurry was filtered without standing still (0 hours of standing) and the case where it was filtered after standing still for 72 hours, for ash A, the filtration time when not standing was However, the filtration time after standing for 72 hours is 22 seconds. In addition, for ash B, the filtration time is 7 seconds when not left standing, but the filtration time after standing still for 72 hours is 10 seconds, and the filtration time after standing still is 10 seconds for both ash A and ash B. become longer.
スラリーを静置せずに濾過すると、灰粒子がスラリー中に分散した状態で濾過されるので、スラリーの水分が抜けやすいが、スラリーを長時間静置すると、図4に示すように、沈降汚泥の上側に粘土状の堆積層が形成されるのが観察される。スラリーの水分がこの堆積層を通過し難くなるため濾過時間が長くなると思われる。 If the slurry is filtered without standing still, the ash particles will be filtered while being dispersed in the slurry, so water in the slurry will easily come out. However, if the slurry is left standing for a long time, it will become settled sludge, as shown in Figure 4. A clay-like sedimentary layer is observed to be formed on the upper side. It is thought that the filtration time becomes longer because it becomes difficult for the moisture in the slurry to pass through this deposited layer.
本発明の脱塩洗浄方法は、上記知見に基づき、塩素含有灰スラリーを撹拌洗浄した後に、スラリーの静置沈降工程を経ずにベルトフィルターに導入し、移送しながら濾過脱水する。スラリーの静置沈降工程を経ずに濾過脱水することによって、従来の沈降後の脱水よりも濾過脱水時間を短縮することができる。また、本発明の脱塩洗浄方法は、静置沈降工程を経ずにベルトフィルターに導入して脱水するので、脱水工程の負担が過大にならないように、スラリーを調製するときの水分量は塩素含有灰の3~5倍量が好ましい。 The desalting and cleaning method of the present invention is based on the above-mentioned findings, and after stirring and cleaning the chlorine-containing ash slurry, the slurry is introduced into a belt filter without going through a static sedimentation step, and is filtered and dehydrated while being transferred. By filtering and dehydrating the slurry without passing through a static settling step, the time for filtration and dehydration can be shorter than in the conventional dehydration after sedimentation. In addition, in the desalination cleaning method of the present invention, water is introduced into a belt filter for dehydration without going through a static sedimentation process, so in order to avoid an excessive burden on the dehydration process, the amount of water when preparing the slurry is limited to chlorine. The amount is preferably 3 to 5 times the amount of ash contained.
本発明の脱塩方法によれば、濾過時間が短く、塩素含有灰の脱塩処理を迅速に進めることができ、脱塩設備の処理能力を高めることができる。 According to the desalination method of the present invention, the filtration time is short, the desalination treatment of chlorine-containing ash can proceed quickly, and the processing capacity of the desalination equipment can be increased.
以下、本発明の実施例を示す。なお、粒径0.045mm未満の微粒子の割合はJIS Z8801-1試験用ふるい規格にある公称目開き45μmのふるいにて分級したときの篩下の灰重量と灰の全重量の割合から算出した。
Examples of the present invention will be shown below. The proportion of fine particles with a particle size of less than 0.045 mm was calculated from the ratio of the weight of ash under the sieve to the total weight of ash when classified using a sieve with a nominal opening of 45 μm according to the JIS Z8801-1 test sieve standard. .
〔実施例1〕
粒径0.045mm未満の微粒子の割合を、(イ)2wt%未満、(ロ)50wt%、(ハ)100wt%に調整した灰Aを用い、固形分濃度約90g/Lの3種類のスラリーを調製した。これらのスラリーを振とう器に入れ、15分若しくは300分間振とうし、スラリーの水分が50wt%以下になるまで濾過脱水した。この濾過時間を図1に示した。図示するように、スラリー(イ)の濾過時間は13秒、スラリー(ロ)の濾過時間は335秒、スラリー(ハ)の濾過時間は823秒であった。
[Example 1]
Using ash A in which the proportion of fine particles with a particle size of less than 0.045 mm was adjusted to (a) less than 2 wt%, (b) 50 wt%, and (c) 100 wt%, three types of slurry with a solid content concentration of approximately 90 g/L were prepared. was prepared. These slurries were placed in a shaker, shaken for 15 minutes or 300 minutes, and filtered and dehydrated until the water content of the slurry became 50 wt% or less. This filtration time is shown in FIG. As shown in the figure, the filtration time for slurry (a) was 13 seconds, the filtration time for slurry (b) was 335 seconds, and the filtration time for slurry (c) was 823 seconds.
〔実施例2〕
灰Aと灰Bについて、おのおの粒径0.2~1.0mmの灰を用い、固形分濃度約90g/Lのスラリーを調製し、同一の撹拌洗浄槽を用い、15分間撹拌した場合と300分撹拌した場合の粒径0.045mm未満の微粒子の割合を調べた。この結果を図2に示した。図示するように、灰Aについて、粒径0.045mm未満の微粒子の割合は、300分の撹拌時間では12wt%であり、15分の撹拌時間では6wt%であった。灰Bについては、粒径0.045mm未満の微粒子の割合は、300分の撹拌時間では27wt%であり、15分の撹拌時間では2wt%であった。
[Example 2]
For ash A and ash B, a slurry with a solid content concentration of approximately 90 g/L was prepared using ash with a particle size of 0.2 to 1.0 mm, and the slurry was stirred for 15 minutes using the same stirring washing tank. The proportion of fine particles with a particle size of less than 0.045 mm after stirring for 1 minute was investigated. The results are shown in FIG. As shown in the figure, for ash A, the proportion of fine particles with a particle size of less than 0.045 mm was 12 wt% at a stirring time of 300 minutes, and 6 wt% at a stirring time of 15 minutes. For ash B, the proportion of fine particles with a particle size of less than 0.045 mm was 27 wt% at a stirring time of 300 minutes, and 2 wt% at a stirring time of 15 minutes.
〔実施例3〕
実施例2と同様の15分間撹拌した灰Aのスラリー、灰Bのスラリーについて、容器に入れ、0時間(静置なし)または72時間静置し、スラリーの水分が50wt%以下になるまで濾過脱水した。この濾過時間を図3示した。図示するように、灰Aについて、静置しないときの濾過時間は約12時間であり、72時間静置した後の濾過時間は22秒であった。灰Bについて、静置しないときの濾過時間は7秒であり、72時間静置後の濾過時間は10秒であった。また、灰Aについて、72時間静置した試料の沈降汚泥の状態を図4に示す。図示するように、沈降汚泥の上側に粘土状の堆積層が観察された。静置しない試料は沈降汚泥がみられず、灰粒子がスラリー中に分散した状態であった。
[Example 3]
The ash A slurry and ash B slurry stirred for 15 minutes as in Example 2 were placed in a container, allowed to stand for 0 hours (no standing) or 72 hours, and filtered until the water content of the slurry became 50 wt% or less. Dehydrated. This filtration time is shown in FIG. As shown in the figure, for ash A, the filtration time without standing was about 12 hours, and the filtration time after standing for 72 hours was 22 seconds. Regarding ash B, the filtration time without standing was 7 seconds, and the filtration time after 72 hours of standing was 10 seconds. Furthermore, regarding ash A, the state of the settled sludge of the sample left undisturbed for 72 hours is shown in FIG. As shown in the figure, a clay-like sediment layer was observed above the settled sludge. In the samples that were not allowed to stand still, no settled sludge was observed, and ash particles were dispersed in the slurry.
Claims (3)
The method for desalting and cleaning chlorine-containing ash according to claim 1 or 2, wherein 3 to 5 times the amount of water is added to the chlorine-containing ash to form a slurry.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP2020032490A JP7392913B2 (en) | 2020-02-27 | 2020-02-27 | Demineralization cleaning method for chlorine-containing ash |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP2020032490A JP7392913B2 (en) | 2020-02-27 | 2020-02-27 | Demineralization cleaning method for chlorine-containing ash |
Publications (2)
Publication Number | Publication Date |
---|---|
JP2021133322A JP2021133322A (en) | 2021-09-13 |
JP7392913B2 true JP7392913B2 (en) | 2023-12-06 |
Family
ID=77659960
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP2020032490A Active JP7392913B2 (en) | 2020-02-27 | 2020-02-27 | Demineralization cleaning method for chlorine-containing ash |
Country Status (1)
Country | Link |
---|---|
JP (1) | JP7392913B2 (en) |
Citations (7)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2002239530A (en) | 2001-02-14 | 2002-08-27 | Fuji Kikai Kk | Method for treating incineration ash and incineration ash washing liquid |
JP2003080199A (en) | 2001-09-11 | 2003-03-18 | Fuji Kikai Kk | Method for washing treatment of ash |
JP2004358288A (en) | 2003-06-02 | 2004-12-24 | Taiheiyo Cement Corp | Method for washing/desalting incineration ash |
JP2005224672A (en) | 2004-02-10 | 2005-08-25 | Chugoku Electric Power Co Inc:The | Dehydrating system and method for clinker and fly ash sludge |
JP2008055395A (en) | 2006-09-04 | 2008-03-13 | Fujita Corp | Method of treating burned ash |
JP2017148720A (en) | 2016-02-24 | 2017-08-31 | 太平洋セメント株式会社 | Processing device and processing method for chlorine-containing dust |
JP2021053582A (en) | 2019-09-30 | 2021-04-08 | 三菱マテリアル株式会社 | Desalting washing method of chlorine containing ash and desalting washing device |
Family Cites Families (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2865958B2 (en) * | 1992-10-26 | 1999-03-08 | 三菱重工業株式会社 | Detoxification method of fly ash |
-
2020
- 2020-02-27 JP JP2020032490A patent/JP7392913B2/en active Active
Patent Citations (7)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2002239530A (en) | 2001-02-14 | 2002-08-27 | Fuji Kikai Kk | Method for treating incineration ash and incineration ash washing liquid |
JP2003080199A (en) | 2001-09-11 | 2003-03-18 | Fuji Kikai Kk | Method for washing treatment of ash |
JP2004358288A (en) | 2003-06-02 | 2004-12-24 | Taiheiyo Cement Corp | Method for washing/desalting incineration ash |
JP2005224672A (en) | 2004-02-10 | 2005-08-25 | Chugoku Electric Power Co Inc:The | Dehydrating system and method for clinker and fly ash sludge |
JP2008055395A (en) | 2006-09-04 | 2008-03-13 | Fujita Corp | Method of treating burned ash |
JP2017148720A (en) | 2016-02-24 | 2017-08-31 | 太平洋セメント株式会社 | Processing device and processing method for chlorine-containing dust |
JP2021053582A (en) | 2019-09-30 | 2021-04-08 | 三菱マテリアル株式会社 | Desalting washing method of chlorine containing ash and desalting washing device |
Also Published As
Publication number | Publication date |
---|---|
JP2021133322A (en) | 2021-09-13 |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
DE102005037831A1 (en) | Purifying heavy metal-containing waste water from processing and cleaning of fishing nets, by flocculation, solid-liquid separation, precipitation of heavy metals and sedimentation | |
JP5761544B1 (en) | Method and apparatus for desalinating chlorine-containing ash | |
WO2019241413A1 (en) | Methods and processes for lignin isolation/extraction | |
JP2007083158A (en) | Membrane filtering device with solid separator, and water treating method using it | |
US20110135797A1 (en) | Flocculation method | |
JP7392913B2 (en) | Demineralization cleaning method for chlorine-containing ash | |
JP4522297B2 (en) | Method and apparatus for treating wastewater containing inorganic suspended particles | |
JP3340029B2 (en) | Method of treating wastewater containing SiO2 | |
JP5770830B2 (en) | Water treatment by ballast flocculation using natural flocculants | |
JP4526078B2 (en) | Method for treating wastewater containing inorganic suspended particles | |
JP3693273B2 (en) | Construction aggregate cleaning waste mud dewatering method | |
KR101879208B1 (en) | High-rate Water Treatment Method and Equipment using Mixed Mineral As Weighting Agent | |
JP2989964B2 (en) | Radioactive waste liquid treatment equipment | |
JPH0576876A (en) | Treatment of waste water containing fluorine and manganese | |
JPH03118896A (en) | Method for removing the solid phase from a liquid substance, particularly waste water purification method | |
KR20180050254A (en) | High-rate Water Treatment Method and Equipment using Mixed Mineral As Weighting Agent | |
JP7184622B2 (en) | Method for recovering gypsum dihydrate from waste gypsum board | |
JP2015054287A (en) | Sludge treatment method | |
JP7075718B2 (en) | Purified water sludge treatment agent, purified water sludge treatment method and purified water sludge treatment equipment | |
JP2861370B2 (en) | Wastewater treatment method | |
JP2010075928A (en) | Treatment method and treatment device for fluorine-containing waste water | |
JPH06343999A (en) | Dehydration process for sludge | |
WO2019241408A1 (en) | Methods and processes for lignin isolation/extraction | |
JPH04176384A (en) | Treatment of drainage | |
WO2010032212A1 (en) | Treatment of hydrometallurgical process streams for removal of suspended fine particles |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
A521 | Request for written amendment filed |
Free format text: JAPANESE INTERMEDIATE CODE: A523 Effective date: 20201006 |
|
A521 | Request for written amendment filed |
Free format text: JAPANESE INTERMEDIATE CODE: A821 Effective date: 20201006 |
|
A621 | Written request for application examination |
Free format text: JAPANESE INTERMEDIATE CODE: A621 Effective date: 20220930 |
|
A977 | Report on retrieval |
Free format text: JAPANESE INTERMEDIATE CODE: A971007 Effective date: 20230517 |
|
A131 | Notification of reasons for refusal |
Free format text: JAPANESE INTERMEDIATE CODE: A131 Effective date: 20230522 |
|
A521 | Request for written amendment filed |
Free format text: JAPANESE INTERMEDIATE CODE: A523 Effective date: 20230629 |
|
A131 | Notification of reasons for refusal |
Free format text: JAPANESE INTERMEDIATE CODE: A131 Effective date: 20230822 |
|
A521 | Request for written amendment filed |
Free format text: JAPANESE INTERMEDIATE CODE: A523 Effective date: 20231007 |
|
TRDD | Decision of grant or rejection written | ||
A01 | Written decision to grant a patent or to grant a registration (utility model) |
Free format text: JAPANESE INTERMEDIATE CODE: A01 Effective date: 20231025 |
|
A61 | First payment of annual fees (during grant procedure) |
Free format text: JAPANESE INTERMEDIATE CODE: A61 Effective date: 20231107 |
|
R150 | Certificate of patent or registration of utility model |
Ref document number: 7392913 Country of ref document: JP Free format text: JAPANESE INTERMEDIATE CODE: R150 |