JPH07246398A - Method for caking sewage dehydrated sludge - Google Patents

Method for caking sewage dehydrated sludge

Info

Publication number
JPH07246398A
JPH07246398A JP4088394A JP4088394A JPH07246398A JP H07246398 A JPH07246398 A JP H07246398A JP 4088394 A JP4088394 A JP 4088394A JP 4088394 A JP4088394 A JP 4088394A JP H07246398 A JPH07246398 A JP H07246398A
Authority
JP
Japan
Prior art keywords
sewage
sludge
zeolite
incinerated ash
incineration ash
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.)
Pending
Application number
JP4088394A
Other languages
Japanese (ja)
Inventor
Yuichi Ikeda
裕一 池田
Hirokazu Tsuboi
博和 坪井
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
NGK Insulators Ltd
Original Assignee
NGK Insulators Ltd
Priority date (The priority date 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 date listed.)
Filing date
Publication date
Application filed by NGK Insulators Ltd filed Critical NGK Insulators Ltd
Priority to JP4088394A priority Critical patent/JPH07246398A/en
Publication of JPH07246398A publication Critical patent/JPH07246398A/en
Pending legal-status Critical Current

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  • Treatment Of Sludge (AREA)

Abstract

PURPOSE:To cake a sewage dehydrated sludge while preventing the elution of various harmful materials and without incresing the treating amt. and the reclamation amt. CONSTITUTION:Incinerated ash zeolite obtained from sewage sludge incinerated ash, cement and water are added to a sewage dehydrated sludge, kneaded and then cured to form a cake. The indinerated ash zeolite is hydrothermally synthsized by mixing the incinerated ash with an aq. soln. of an alkali metal hydroxide such as NaOH and heating the mixture. Sewage sludge incinerated ash or the molten slag of sewage sludge incinerated ash can be added as well as the incinerated ash zeolite.

Description

【発明の詳細な説明】Detailed Description of the Invention

【0001】[0001]

【産業上の利用分野】本発明は、下水処理場から発生す
る下水脱水汚泥などを系外に有害物質を出さないような
安定な固化物とすることができる下水脱水汚泥の固化処
理方法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 for solidifying sewage dewatering sludge, which can form a stable solidified product which does not emit harmful substances out of the system such as sewage dewatering sludge generated from a sewage treatment plant. Is.

【0002】[0002]

【従来の技術】下水処理場から大量に発生する下水汚泥
の処理方法として、下水脱水汚泥を焼却減容した焼却灰
をセメントとともに下水汚泥に混練して、無機質の土壌
に近い性質として埋め立て処分する方法が知られてい
る。またシアン、六価クロム等の重金属化合物を含有す
る産業廃棄物の処理方法として、セメントと天然ゼオラ
イトと水とを廃棄物のスラッジに混練し、固化する方法
が知られている。
2. Description of the Related Art As a method of treating a large amount of sewage sludge generated from a sewage treatment plant, incineration ash obtained by incineration and reducing the volume of sewage dewatered sludge is mixed with cement into sewage sludge and landfilled as a property similar to inorganic soil. The method is known. As a method for treating industrial waste containing heavy metal compounds such as cyanide and hexavalent chromium, a method is known in which cement, natural zeolite, and water are kneaded with waste sludge and solidified.

【0003】しかし前者の方法は重金属化合物、アンモ
ニア態窒素、リン等の溶出防止にはある程度の効果があ
るが、COD原因物質となる有機物等の溶出防止にはあ
まり効果がない。このため、埋め立て処分を行うと付近
の水域を富栄養化し、赤潮の発生を招くおそれがある。
また後者の方法は重金属化合物や臭気の漏出を防止でき
る効果があるものの、系外から多量の天然ゼオライトを
持ち込むため、処理量が増大して処理設備が大型化する
とともに、埋め立て量も増大するという欠点がある。
However, the former method has some effect in preventing the elution of heavy metal compounds, ammonia nitrogen, phosphorus, etc., but is not so effective in preventing the elution of organic substances, etc., which are COD-causing substances. For this reason, landfill disposal may eutrophicate nearby waters and cause red tides.
Although the latter method has the effect of preventing the leakage of heavy metal compounds and odors, since a large amount of natural zeolite is brought in from outside the system, the treatment amount increases, the treatment equipment becomes larger, and the landfill amount also increases. There are drawbacks.

【0004】[0004]

【発明が解決しようとする課題】本発明は上記した従来
の問題点を解決し、重金属化合物、アンモニア態窒素、
リン、有機物、COD原因物質等の溶出を防止すること
ができ、しかも処理量や埋め立て量を増加させることの
ない下水脱水汚泥の固化処理方法を提供するためになさ
れたものである。
DISCLOSURE OF THE INVENTION The present invention solves the above-mentioned conventional problems, and solves the problems of heavy metal compounds, ammonia nitrogen,
The object of the present invention is to provide a method for solidifying sewage dewatered sludge that can prevent the elution of phosphorus, organic substances, COD-causing substances, and the like, and that does not increase the treatment amount or landfill amount.

【0005】[0005]

【課題を解決するための手段】上記の課題を解決するた
めになされた請求項1の発明は、下水脱水汚泥に対し
て、下水汚泥焼却灰を原料とする焼却灰ゼオライトとセ
メントとを添加して混練した後、養生することにより固
化物とすることを特徴とするものである。また請求項2
の発明は、下水脱水汚泥と下水汚泥焼却灰に対して、下
水汚泥焼却灰を原料とする焼却灰ゼオライトとセメント
とを添加して混練した後、養生することにより固化物と
することを特徴とするものである。さらに請求項3の発
明は、下水脱水汚泥と下水汚泥焼却灰と下水汚泥焼却灰
溶融スラグに対して、下水汚泥焼却灰を原料とする焼却
灰ゼオライトとセメントとを添加して混練した後、養生
することにより固化物とすることを特徴とするものであ
る。なお、いずれの場合にも必要に応じて水を添加して
混練することができ、焼却灰ゼオライトとセメントと水
とを添加して混練した後、更に焼却灰ゼオライトを再混
練し、養生する方法を取ることもできる。また、実施例
に示すように焼却灰ゼオライトの添加量は固化物重量の
20〜50%とすることが好ましい。
In order to solve the above-mentioned problems, the invention of claim 1 is one in which incineration ash zeolite made from sewage sludge incinerator ash and cement are added to sewage dehydrated sludge. It is characterized in that it is solidified by curing after kneading. Claim 2
The invention of, with respect to sewage dewatered sludge and sewage sludge incineration ash, after adding and kneading incineration ash zeolite and cement using sewage sludge incineration ash as a raw material, characterized by curing to a solidified product To do. Furthermore, the invention of claim 3 is the curing after sewage dewatered sludge, sewage sludge incineration ash, and sewage sludge incineration ash molten slag are kneaded by adding incineration ash zeolite and cement made from sewage sludge incineration ash as a raw material. It is characterized in that it is made into a solidified product. In any case, water can be added and kneaded as needed, and after kneading by adding incinerated ash zeolite, cement, and water, the incinerated ash zeolite is re-kneaded and cured. You can also take In addition, as shown in the examples, the amount of incinerated ash zeolite added depends on the weight of the solidified matter.
It is preferably 20 to 50%.

【0006】[0006]

【作用】本発明は、下水脱水汚泥等に対して下水脱水汚
泥焼却灰を原料とする焼却灰ゼオライトとセメントを添
加する点に特徴がある。この焼却灰ゼオライトは、焼却
灰をNaOH等のアルカリ金属水酸化物の水溶液と混合、加
熱して水熱合成することにより製造されるものであり、
天然ゼオライトと同等以上の塩基置換容量(CEC値) を持
つ。この焼却灰ゼオライトを下水脱水汚泥等に対してセ
メントとともに添加すると、下水脱水汚泥中の重金属化
合物、アンモニア態窒素、リン、有機物、COD原因物
質等を吸着し、セメントにより固化された固化物から系
外へこれらの有害物質が溶出することを防止することが
できる。しかも天然ゼオライトとは異なり、本発明にお
いては下水汚泥焼却灰を原料とする焼却灰ゼオライトを
使用するので、全体としての処理量や埋め立て量が増加
することがない。本発明のフローを図1に示す。
The present invention is characterized in that incineration ash zeolite made from sewage dewatered sludge incineration ash and cement are added to sewage dewatered sludge and the like. This incinerated ash zeolite is produced by mixing incinerated ash with an aqueous solution of an alkali metal hydroxide such as NaOH, heating and hydrothermally synthesizing the ash.
It has a base substitution capacity (CEC value) equal to or higher than that of natural zeolite. When this incinerated ash zeolite is added to sewage dewatered sludge along with cement, it absorbs heavy metal compounds, ammonia nitrogen, phosphorus, organic substances, COD-causing substances, etc. in sewage dewatered sludge, and the system is formed from the solidified product solidified by cement. It is possible to prevent these harmful substances from being eluted to the outside. Moreover, unlike natural zeolite, in the present invention, since incineration ash zeolite made from sewage sludge incineration ash is used, the total treatment amount and landfill amount do not increase. The flow of the present invention is shown in FIG.

【0007】[0007]

【実施例】〔実施例1〕まず下水処理場から発生した脱
水された下水脱水汚泥100 重量部に対して、汚泥固化用
のセメント15重量部と、下水脱水汚泥焼却灰30重量部と
を添加し、水とともに混練し、養生した。一方これとは
別に、下水脱水汚泥焼却灰36重量部に対して、80g/l の
NaOHを181 重量部加え、90℃で7時間加熱してゼオライ
トを合成し、焼却灰ゼオライトを得た。この焼却灰ゼオ
ライト5g を、前記の養生物20gに加えて再混練し、養
生することにより固化物を得た。これを試料1とした。
試料1における焼却灰ゼオライトの添加量は固化物重量
の20%である。
[Example 1] First, to 100 parts by weight of dehydrated sewage dewatered sludge generated from a sewage treatment plant, 15 parts by weight of cement for sludge solidification and 30 parts by weight of incinerated ash of dewatered sludge were added. Then, it was kneaded with water and cured. Separately from this, 80 g / l of sewage dewatered sludge incineration ash 36 parts by weight
181 parts by weight of NaOH was added and heated at 90 ° C. for 7 hours to synthesize zeolite to obtain incinerated ash zeolite. 5 g of this incinerated ash zeolite was added to 20 g of the above-mentioned aquatic organism, re-kneaded, and cured to obtain a solidified product. This was designated as Sample 1.
The amount of incinerated ash zeolite added in Sample 1 was 20% of the weight of the solidified product.

【0008】次に焼却灰ゼオライト15g を、前記の養生
物20g に加えて再混練し養生することにより固化物を得
た。これを試料2とした。試料2における焼却灰ゼオラ
イトの添加量は固化物重量の43%である。さらに比較の
ために焼却灰ゼオライトを混入しない前記の混練物を試
料3とした。焼却灰ゼオライトの添加量は0%である。
Next, 15 g of incinerated ash zeolite was added to 20 g of the above-mentioned aquatic organism, re-kneaded and aged to obtain a solidified product. This was designated as Sample 2. The amount of incinerated ash zeolite added in Sample 2 was 43% of the weight of the solidified product. Further, for comparison, the above kneaded product containing no incinerated ash zeolite was designated as Sample 3. The amount of incinerated ash zeolite added is 0%.

【0009】これらの各試料20g に対して蒸留水100mL
を加えて6時間攪拌し、その溶出液を遠心分離して上澄
水を得た。この上澄水中のNH4 + 濃度を測定したとこ
ろ、試料1については14.1mg/l、試料2については9.0
mg/lであったが、焼却灰ゼオライトを混入しない試料3
については15.8mg/lであった。この結果、試料1ではNH
4 + の溶出防止率は11%、試料2では43%であることが
分かる。
100 mL of distilled water for 20 g of each of these samples
Was added and the mixture was stirred for 6 hours, and the eluate was centrifuged to obtain supernatant water. The NH 4 + concentration in this supernatant water was measured and found to be 14.1 mg / l for sample 1 and 9.0 for sample 2.
Although it was mg / l, sample 3 containing no incinerated ash zeolite
Was 15.8 mg / l. As a result, NH
It can be seen that the dissolution rate of 4 + is 11% and that of sample 2 is 43%.

【0010】〔実施例2〕下水脱水汚泥に対して、焼却
灰、セメント、焼却灰ゼオライト等を表1に示されると
おり添加して混合攪拌し、試料4と試料5を得た。これ
らの試料4と試料5に対して比較例である試料3ととも
に溶出試験を行った結果、表2に示すとおりの結果とな
った。いずれも優れた溶出防止を持つことが分かる。な
お、溶出防止効果は試料3の溶出量をベースとして算出
した。
[Example 2] Samples 4 and 5 were obtained by adding incinerated ash, cement, incinerated ash zeolite, etc. to the sewage dewatered sludge as shown in Table 1 and mixing and stirring. As a result of performing an elution test on Sample 4 and Sample 5 together with Sample 3 which is a comparative example, the results shown in Table 2 were obtained. It can be seen that all have excellent elution prevention. The elution prevention effect was calculated based on the elution amount of Sample 3.

【0011】[0011]

【表1】 [Table 1]

【0012】[0012]

【表2】 [Table 2]

【0013】[0013]

【発明の効果】以上に説明したように、本発明の下水脱
水汚泥の固化処理方法によれば、焼却灰ゼオライトの添
加によって固化物中の重金属化合物、アンモニア態窒
素、リン、COD原因物質等を吸着し、それらの溶出を
防止することができるから、固化物の埋め立て後におけ
る系外への有害物質の漏出を防止することができる。し
かもこの焼却灰ゼオライトは下水脱水汚泥焼却灰を原料
として合成されたものであるため、全体としての処理量
や埋め立て量を増加させることがない利点がある。よっ
て本発明は従来の問題点を解決した下水脱水汚泥の固化
処理方法として、価値の大きいものである。
As described above, according to the method for solidifying sewage dewatered sludge of the present invention, the addition of incinerated ash zeolite can remove heavy metal compounds, ammonia nitrogen, phosphorus, COD-causing substances, etc. in the solidified product. Since they can be adsorbed and their elution can be prevented, it is possible to prevent leakage of harmful substances to the outside of the system after the solidified material is filled up. Moreover, since this incinerated ash zeolite is synthesized by using sewage dewatered sludge incinerated ash as a raw material, there is an advantage that the total treatment amount and landfill amount are not increased. Therefore, the present invention is of great value as a method for solidifying sewage dewatered sludge that solves the conventional problems.

【図面の簡単な説明】[Brief description of drawings]

【図1】本発明のフローチャートである。FIG. 1 is a flow chart of the present invention.

Claims (6)

【特許請求の範囲】[Claims] 【請求項1】 下水脱水汚泥に対して、下水汚泥焼却灰
を原料とする焼却灰ゼオライトとセメントとを添加して
混練した後、養生することにより固化物とすることを特
徴とする下水脱水汚泥の固化処理方法。
1. A sewage dewatered sludge, which is obtained by adding incineration ash zeolite and sewage sludge incinerated ash as a raw material to sewage dewatered sludge, kneading the mixture, and then curing it to form a solidified product. Solidification treatment method.
【請求項2】 下水脱水汚泥と下水汚泥焼却灰に対し
て、下水汚泥焼却灰を原料とする焼却灰ゼオライトとセ
メントとを添加して混練した後、養生することにより固
化物とすることを特徴とする下水脱水汚泥の固化処理方
法。
2. A sewage dewatered sludge and a sewage sludge incineration ash are mixed with incineration ash zeolite and cement made from sewage sludge incineration ash as a raw material, kneaded, and then cured to form a solidified product. A method for solidifying sewage dehydrated sludge.
【請求項3】 下水脱水汚泥と下水汚泥焼却灰と下水汚
泥焼却灰溶融スラグに対して、下水汚泥焼却灰を原料と
する焼却灰ゼオライトとセメントとを添加して混練した
後、養生することにより固化物とすることを特徴とする
下水脱水汚泥の固化処理方法。
3. The sewage dewatered sludge, the sewage sludge incineration ash, and the sewage sludge incineration ash molten slag are mixed with incineration ash zeolite and cement made from sewage sludge incineration ash as raw materials, and then cured. A method for solidifying sewage dewatered sludge, which is characterized in that it is a solidified product.
【請求項4】 水を加えて混練する請求項1〜3のいず
れかに記載の下水脱水汚泥の固化処理方法。
4. The method for solidifying sewage dewatered sludge according to claim 1, wherein water is added and kneaded.
【請求項5】 焼却灰ゼオライトの添加量を固化物重量
の20〜50%とした請求項1〜4のいずれかに記載の下水
脱水汚泥の固化処理方法。
5. The method for solidifying sewage dewatered sludge according to claim 1, wherein the amount of the incinerated ash zeolite added is 20 to 50% of the weight of the solidified product.
【請求項6】 請求項1〜4のいずれかの方法により得
られた固化物と焼却灰ゼオライトとを再混練し、養生す
る下水脱水汚泥の固化処理方法。
6. A method for solidifying sewage dehydrated sludge, which comprises re-kneading and curing the solidified product obtained by the method according to claim 1 and incinerated ash zeolite.
JP4088394A 1994-03-11 1994-03-11 Method for caking sewage dehydrated sludge Pending JPH07246398A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP4088394A JPH07246398A (en) 1994-03-11 1994-03-11 Method for caking sewage dehydrated sludge

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP4088394A JPH07246398A (en) 1994-03-11 1994-03-11 Method for caking sewage dehydrated sludge

Publications (1)

Publication Number Publication Date
JPH07246398A true JPH07246398A (en) 1995-09-26

Family

ID=12592919

Family Applications (1)

Application Number Title Priority Date Filing Date
JP4088394A Pending JPH07246398A (en) 1994-03-11 1994-03-11 Method for caking sewage dehydrated sludge

Country Status (1)

Country Link
JP (1) JPH07246398A (en)

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