JPS5837040B2 - Sludge dewatering method - Google Patents
Sludge dewatering methodInfo
- Publication number
- JPS5837040B2 JPS5837040B2 JP52109274A JP10927477A JPS5837040B2 JP S5837040 B2 JPS5837040 B2 JP S5837040B2 JP 52109274 A JP52109274 A JP 52109274A JP 10927477 A JP10927477 A JP 10927477A JP S5837040 B2 JPS5837040 B2 JP S5837040B2
- Authority
- JP
- Japan
- Prior art keywords
- sludge
- dewatering
- hydrochloric acid
- addition
- flocs
- 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.)
- Expired
Links
- 239000010802 sludge Substances 0.000 title claims description 40
- 238000000034 method Methods 0.000 title claims description 15
- VEXZGXHMUGYJMC-UHFFFAOYSA-N Hydrochloric acid Chemical compound Cl VEXZGXHMUGYJMC-UHFFFAOYSA-N 0.000 claims description 23
- 229910021578 Iron(III) chloride Inorganic materials 0.000 claims description 9
- RBTARNINKXHZNM-UHFFFAOYSA-K iron trichloride Chemical compound Cl[Fe](Cl)Cl RBTARNINKXHZNM-UHFFFAOYSA-K 0.000 claims description 9
- 239000007787 solid Substances 0.000 claims description 6
- 239000010800 human waste Substances 0.000 claims description 2
- 239000010842 industrial wastewater Substances 0.000 claims description 2
- 239000010865 sewage Substances 0.000 claims description 2
- 239000002351 wastewater Substances 0.000 claims 1
- 159000000007 calcium salts Chemical class 0.000 description 9
- 230000018044 dehydration Effects 0.000 description 8
- 238000006297 dehydration reaction Methods 0.000 description 8
- 239000002253 acid Substances 0.000 description 6
- 238000001914 filtration Methods 0.000 description 6
- 238000003756 stirring Methods 0.000 description 5
- 238000010586 diagram Methods 0.000 description 3
- 239000007788 liquid Substances 0.000 description 3
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 3
- 150000002505 iron Chemical class 0.000 description 2
- 235000014413 iron hydroxide Nutrition 0.000 description 2
- NCNCGGDMXMBVIA-UHFFFAOYSA-L iron(ii) hydroxide Chemical compound [OH-].[OH-].[Fe+2] NCNCGGDMXMBVIA-UHFFFAOYSA-L 0.000 description 2
- 229920000642 polymer Polymers 0.000 description 2
- 238000000926 separation method Methods 0.000 description 2
- 239000000126 substance Substances 0.000 description 2
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 1
- 150000007513 acids Chemical class 0.000 description 1
- 230000015572 biosynthetic process Effects 0.000 description 1
- AXCZMVOFGPJBDE-UHFFFAOYSA-L calcium dihydroxide Chemical compound [OH-].[OH-].[Ca+2] AXCZMVOFGPJBDE-UHFFFAOYSA-L 0.000 description 1
- 239000000920 calcium hydroxide Substances 0.000 description 1
- 229910001861 calcium hydroxide Inorganic materials 0.000 description 1
- 235000011116 calcium hydroxide Nutrition 0.000 description 1
- 239000000701 coagulant Substances 0.000 description 1
- 230000001112 coagulating effect Effects 0.000 description 1
- 238000007796 conventional method Methods 0.000 description 1
- 238000005260 corrosion Methods 0.000 description 1
- 230000007797 corrosion Effects 0.000 description 1
- 230000000694 effects Effects 0.000 description 1
- 239000008394 flocculating agent Substances 0.000 description 1
- 238000002347 injection Methods 0.000 description 1
- 239000007924 injection Substances 0.000 description 1
- 159000000014 iron salts Chemical class 0.000 description 1
- 230000029052 metamorphosis Effects 0.000 description 1
- 239000000843 powder Substances 0.000 description 1
- 238000002203 pretreatment Methods 0.000 description 1
- 239000000047 product Substances 0.000 description 1
- 230000001737 promoting effect Effects 0.000 description 1
- 238000004062 sedimentation Methods 0.000 description 1
- 239000000243 solution Substances 0.000 description 1
- 239000006228 supernatant Substances 0.000 description 1
- 238000004065 wastewater treatment Methods 0.000 description 1
Landscapes
- Separation Of Suspended Particles By Flocculating Agents (AREA)
- Treatment Of Sludge (AREA)
Description
【発明の詳細な説明】
本発明は汚泥脱水の前処理をして脱水する汚泥脱水方法
詳しくは汚泥脱水に際し汚泥に塩酸と塩化第二鉄を添加
し汚泥フロックを形成せしめて脱水する汚泥脱水方法6
こ関する。DETAILED DESCRIPTION OF THE INVENTION The present invention provides a sludge dewatering method in which sludge is dehydrated by pre-treatment. More specifically, a sludge dewatering method involves adding hydrochloric acid and ferric chloride to sludge to form sludge flocs during sludge dewatering. 6
Regarding this.
従来分離脱水助剤として汚泥に鉄塩及ひカルシウム塩を
併用使用する方法があるが、カルシウム塩(例えば消石
灰)の添カロ量は汚泥中の汚泥固形分(以前単Cこds
と称す)の平均30重量%(以下、%は全て重量%とす
る)6こも及ぶ多量であって、このカルシウム塩はその
まま脱水ケーキ中に含まれるため脱水ケーキが増量され
ることとなり、従って脱水ケーキの処理量が増加するの
で不具合であり、又カルシウム塩は常温では溶解度が小
さく、瀘布の目詰りを起し易くしかもカルシウム塩は固
体粉状であるので注入量の調節が簡単でない等の欠点を
有する。Conventionally, there is a method of using iron salts and calcium salts in combination with sludge as separation and dewatering aids, but the amount of calories added to calcium salts (e.g. slaked lime) is determined by the sludge solid content (formerly known as monocarbon).
This calcium salt is contained in the dehydrated cake as it is, which increases the weight of the dehydrated cake. This is a problem because the amount of cake to be processed increases, and calcium salts have low solubility at room temperature and easily clog the filter, and since calcium salts are in the form of solid powder, it is not easy to adjust the amount of injection. It has its drawbacks.
又酸と高分子凝集剤を併用するものがあるが、添加後の
攪拌強度、攪拌時間の微かの相違で汚泥フロックの大き
さ、強度が変化するので、その調整に関しよく管理する
必要があり、或いは又攪拌方法により瀘過工程の瀘過速
度、脱水ケーキの含水率が相違するなど操業条件設定、
操業管理が複雑化するなどの欠点を有する。In addition, there are products that use both acid and polymer flocculants, but the size and strength of the sludge flocs change due to slight differences in the stirring intensity and stirring time after addition, so it is necessary to carefully manage the adjustment. Alternatively, operating conditions settings such as the filtration rate of the filtration process and the moisture content of the dehydrated cake may differ depending on the stirring method.
This method has drawbacks such as complicating operational management.
本発明はこれらの欠点を解決するものであり、し尿、下
水、有機性産業廃水等の排水処理における汚泥の脱水方
法6こおいて、汚泥6こ塩酸と塩化第二鉄を添加して脱
水する汚泥脱水方法であって、汚泥を凝集してフロック
を形成せしめ、しかもフロックの大きさ、強度の安定せ
るものが得られるので優れた脱水能率が達成される汚泥
脱水方法を提供することを目的とする。The present invention solves these drawbacks, and includes a method for dewatering sludge in wastewater treatment such as human waste, sewage, and organic industrial wastewater, in which sludge is dehydrated by adding hydrochloric acid and ferric chloride. The object of the present invention is to provide a sludge dewatering method in which sludge is coagulated to form flocs, and the size and strength of the flocs are stabilized, thereby achieving excellent dewatering efficiency. do.
本発明の汚泥脱水方法ζこおいて、先ず汚泥に強酸とし
て塩酸を添加し汚泥のpHを汚泥中のアルカリ度戒分が
、中和できるような範囲、すなわちpH4.3乃至5.
5に調整して汚泥中の親水性ゾルの等重点的変成を生ぜ
しめ、同時6こ鉄の水酸化物の溶解度が大きくならぬ程
度に調整しておき、次に鉄塩として塩化第二鉄( F
e Cl3)を添加して汚泥中に鉄の水酸化物のフロッ
クを発生させ従ってこれに伴なって汚泥のフロックの生
成を促進せしめ、汚泥の固形分の凝集を生せしめるので
ある。In the sludge dewatering method ζ of the present invention, first, hydrochloric acid is added as a strong acid to the sludge, and the pH of the sludge is adjusted to a range where the alkalinity of the sludge can be neutralized, that is, pH 4.3 to 5.
5 to cause isotropic metamorphosis of the hydrophilic sol in the sludge, and at the same time adjust the solubility of iron hydroxide to a level that does not increase, and then add ferric chloride as an iron salt. (F
e Cl3) is added to generate iron hydroxide flocs in the sludge, thereby promoting the formation of sludge flocs and coagulating the solid content of the sludge.
図面は本発明の汚泥脱水方法の説明図であって、汚泥1
1に対しHCI添加2次いでFeCl3添加3を行ない
汚泥フロックを形威せしめたる後、脱水(4)として脱
水機6こよる強制脱水を行ない、脱水ケーキと分離液6
こ分離する。The drawing is an explanatory diagram of the sludge dewatering method of the present invention, in which sludge 1
After adding HCI 2 and then adding 3 FeCl3 to 1 to form sludge flocs, forced dehydration is performed using a dehydrator 6 as dewatering (4) to form a dehydrated cake and a separated liquid 6.
Separate.
尚凝集剤添加後の固液分離の方法として強制脱水の外自
然沈降分離により汚泥固形分と上澄水とに分離してもよ
い。As a method for solid-liquid separation after addition of the flocculant, sludge solids and supernatant water may be separated by natural sedimentation in addition to forced dehydration.
本発明の汚泥脱水方法の実施例として原汚泥の性状が固
形分濃度38%、SS35200ppm1pH 7.
5 0、強熱減量50.9%なる汚泥に35%塩酸を添
加し、5 0 rpmの緩速攪拌を10分間行ない、こ
れに塩化第二鉄溶液を添加し1 2 0 rpmの急速
攪拌を5分間行った。As an example of the sludge dewatering method of the present invention, the properties of raw sludge are as follows: solid content concentration: 38%, SS: 35,200 ppm, 1 pH: 7.
50. Add 35% hydrochloric acid to sludge with ignition loss of 50.9%, stir slowly at 50 rpm for 10 minutes, add ferric chloride solution and stir rapidly at 120 rpm. It lasted 5 minutes.
尚塩酸及び塩化第二鉄の添加量はds当り添加率で3.
0乃至13.0%、および7%とした。The amounts of hydrochloric acid and ferric chloride added are at an addition rate of 3.
0 to 13.0% and 7%.
各添加量6こ対する汚泥の実質**濾過速度(kg d
s/m”−}4r)及びケーキ含水率〔%〕は下表及び
右図に示す通りで、HCl6.5%、FeCl37%の
近傍が最も良好なる値を示す。Actual filtration rate of sludge for each addition amount of 6 kg (kg d
s/m''-}4r) and cake moisture content [%] are as shown in the table below and the figure on the right, and show the best values around 6.5% HCl and 37% FeCl.
そして、含水率及び濾過速度の曲線が交差する点はほぼ
pH3.4と5.5の点であり、その範囲内で脱水すれ
ばよいわけであるが、pHが低すぎると、汚泥がかかっ
たり、汚泥内に浸漬する機具が酸6こより腐蝕されるた
め、pH4.3以上が望ましい。The points where the curves of water content and filtration rate intersect are approximately at pH 3.4 and 5.5, and dehydration can be carried out within that range, but if the pH is too low, sludge may form. Since equipment immersed in sludge is corroded by acid, a pH of 4.3 or higher is desirable.
尚凝集剤添加後の汚泥フロックは大きさ、強度共安定せ
るものが生成された。Furthermore, sludge flocs with stable size and strength were produced after adding the flocculant.
本発明の脱水方法は凝集剤として塩酸を3.0乃至13
0%添加してpHを4.3乃至5.5に調整するととも
にds当り7%の塩化第二鉄を添加して脱水するように
したので、従来のカルシウム塩添加の如く多量用いる必
要はなく、シかもカルシウム塩添加の場合カルシウム塩
がそのまま脱水ケーキに含まれて添加量分だけ脱水ケー
キが増量されるが、塩酸添加に際しては凝集剤による脱
水ケーキの増量が全くないのであって、従来のカルシウ
ム塩添加6こ比し同一汚泥量6こ対し脱水負荷を軽減せ
しめることとなり、しかも実質濾過速度が優れるので脱
水処理能力を向上せしめることができ、又塩酸の添加率
が低<pHを必要以上に低くしないため、酸6こよる機
具の腐蝕が少なく、操業時の薬品ランニングコストを低
減せしめると共6こ塩酸は液状であるため薬注の調節が
容易であり、さらには従来の酸と高分子凝集剤の併用す
るものは汚泥の性状により高分子凝集剤を選定する必要
があり又その選定がむつかしい点があるが、本発明の塩
酸と鉄塩なる塩化第二鉄の併用する方法は汚泥の性状に
対し塩酸6こよりpHの調整を行なって後鉄塩の添加す
ること6こより大きさ、強度の安定せるフロックが得ら
れ、従って脱水性能が安定し、所期の脱水条件で安定せ
る含水率のケーキを得ることができるなどの効果を有す
る。The dehydration method of the present invention uses hydrochloric acid as a coagulant in the range of 3.0 to 13
Since we added 0% to adjust the pH to 4.3 to 5.5 and dehydrated by adding 7% ferric chloride per ds, there is no need to use a large amount as with conventional calcium salt addition. However, when adding calcium salt, the calcium salt is contained in the dehydrated cake as it is, and the weight of the dehydrated cake increases by the amount added, but when adding hydrochloric acid, there is no increase in the weight of the dehydrated cake due to the flocculant, which is different from the conventional method. The addition of calcium salt reduces the dewatering load for the same amount of sludge (6 ml), and since the actual filtration rate is excellent, the dehydration processing capacity can be improved, and the addition rate of hydrochloric acid is low < pH higher than necessary Since the acid does not become too low, there is less corrosion of equipment caused by acid 6, which reduces chemical running costs during operation.Since 6, 6, hydrochloric acid is in liquid form, it is easy to adjust the chemical dosing, and furthermore, it is less expensive than conventional acids. When using a molecular flocculant in combination, it is necessary to select a polymer flocculant depending on the properties of the sludge, and selection is difficult. After adjusting the pH with hydrochloric acid and adding iron salt, it is possible to obtain flocs with stable size and strength, and therefore with stable dehydration performance and stable water content under the desired dehydration conditions. It has the effect of being able to obtain a cake of a certain amount.
第1図は本発明の一実施例を示す説明図、第2図はpH
4こ対するケーキ含水率と実質濾過速度の関係図である
。
1・・・・・・汚泥、2・・・・・・}−] C d添
加、3・・・・・・FeCl3添加、4・・・・・・脱
水。Figure 1 is an explanatory diagram showing one embodiment of the present invention, Figure 2 is a pH
FIG. 4 is a diagram showing the relationship between cake moisture content and actual filtration rate. 1...Sludge, 2...}-] C d addition, 3... FeCl3 addition, 4... Dehydration.
Claims (1)
発生する汚泥の脱水方法において、汚泥に、塩酸を添加
してpH 4.3乃至5,5に調整するとともに、汚泥
固形分当り7、O重量%の塩化第二鉄を添加して脱水す
ることを特徴とする汚泥脱水方法。1 In a method for dewatering sludge generated in the treatment of wastewater such as human waste, sewage, and organic industrial wastewater, hydrochloric acid is added to the sludge to adjust the pH to 4.3 to 5.5, and the pH is adjusted to 7.0 O per solid content of the sludge. A sludge dewatering method characterized by dewatering by adding ferric chloride in an amount of % by weight.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP52109274A JPS5837040B2 (en) | 1977-09-10 | 1977-09-10 | Sludge dewatering method |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP52109274A JPS5837040B2 (en) | 1977-09-10 | 1977-09-10 | Sludge dewatering method |
Publications (2)
Publication Number | Publication Date |
---|---|
JPS5442362A JPS5442362A (en) | 1979-04-04 |
JPS5837040B2 true JPS5837040B2 (en) | 1983-08-13 |
Family
ID=14506004
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP52109274A Expired JPS5837040B2 (en) | 1977-09-10 | 1977-09-10 | Sludge dewatering method |
Country Status (1)
Country | Link |
---|---|
JP (1) | JPS5837040B2 (en) |
Families Citing this family (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS5898198A (en) * | 1981-12-07 | 1983-06-10 | Ebara Infilco Co Ltd | Treatment of sewage sludge |
JPS58143900A (en) * | 1982-02-22 | 1983-08-26 | Ebara Infilco Co Ltd | Treatment of organic sludge |
US7029580B2 (en) | 2001-05-14 | 2006-04-18 | Kiyoshi Suzuki | Apparatus for concentrating sludge |
-
1977
- 1977-09-10 JP JP52109274A patent/JPS5837040B2/en not_active Expired
Also Published As
Publication number | Publication date |
---|---|
JPS5442362A (en) | 1979-04-04 |
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