JPH0316700A - Method for dehydrating sludge and chemicals used therefor - Google Patents
Method for dehydrating sludge and chemicals used thereforInfo
- Publication number
- JPH0316700A JPH0316700A JP1153058A JP15305889A JPH0316700A JP H0316700 A JPH0316700 A JP H0316700A JP 1153058 A JP1153058 A JP 1153058A JP 15305889 A JP15305889 A JP 15305889A JP H0316700 A JPH0316700 A JP H0316700A
- Authority
- JP
- Japan
- Prior art keywords
- sludge
- chitosan
- ferric chloride
- flocculant
- dehydrated
- 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
Links
- 239000010802 sludge Substances 0.000 title claims abstract description 41
- 239000000126 substance Substances 0.000 title claims abstract description 8
- 238000000034 method Methods 0.000 title claims description 11
- 229920001661 Chitosan Polymers 0.000 claims abstract description 31
- 229910021578 Iron(III) chloride Inorganic materials 0.000 claims abstract description 24
- RBTARNINKXHZNM-UHFFFAOYSA-K iron trichloride Chemical compound Cl[Fe](Cl)Cl RBTARNINKXHZNM-UHFFFAOYSA-K 0.000 claims abstract description 24
- 150000003839 salts Chemical class 0.000 claims abstract description 11
- 239000007787 solid Substances 0.000 claims abstract description 10
- 239000010865 sewage Substances 0.000 claims abstract description 9
- 239000003814 drug Substances 0.000 claims description 10
- 229940079593 drug Drugs 0.000 claims description 10
- 239000007864 aqueous solution Substances 0.000 claims description 9
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 8
- 239000010801 sewage sludge Substances 0.000 claims 1
- 230000000694 effects Effects 0.000 description 10
- 239000000243 solution Substances 0.000 description 8
- 238000005189 flocculation Methods 0.000 description 5
- 230000016615 flocculation Effects 0.000 description 5
- 230000000052 comparative effect Effects 0.000 description 4
- 230000018044 dehydration Effects 0.000 description 3
- 238000006297 dehydration reaction Methods 0.000 description 3
- 229920000642 polymer Polymers 0.000 description 3
- 238000005054 agglomeration Methods 0.000 description 2
- 230000002776 aggregation Effects 0.000 description 2
- 239000003795 chemical substances by application Substances 0.000 description 2
- 238000005345 coagulation Methods 0.000 description 2
- 230000015271 coagulation Effects 0.000 description 2
- 230000029087 digestion Effects 0.000 description 2
- 239000008394 flocculating agent Substances 0.000 description 2
- 239000007788 liquid Substances 0.000 description 2
- 238000002156 mixing Methods 0.000 description 2
- 239000005416 organic matter Substances 0.000 description 2
- 239000002245 particle Substances 0.000 description 2
- 239000002244 precipitate Substances 0.000 description 2
- 239000000047 product Substances 0.000 description 2
- QTBSBXVTEAMEQO-UHFFFAOYSA-M Acetate Chemical compound CC([O-])=O QTBSBXVTEAMEQO-UHFFFAOYSA-M 0.000 description 1
- 229920002101 Chitin Polymers 0.000 description 1
- 239000005714 Chitosan hydrochloride Substances 0.000 description 1
- VEXZGXHMUGYJMC-UHFFFAOYSA-M Chloride anion Chemical compound [Cl-] VEXZGXHMUGYJMC-UHFFFAOYSA-M 0.000 description 1
- 241000238424 Crustacea Species 0.000 description 1
- 241000238557 Decapoda Species 0.000 description 1
- 229920006318 anionic polymer Polymers 0.000 description 1
- 239000012752 auxiliary agent Substances 0.000 description 1
- 125000002091 cationic group Chemical group 0.000 description 1
- 239000013043 chemical agent Substances 0.000 description 1
- 230000000850 deacetylating effect Effects 0.000 description 1
- 239000003792 electrolyte Substances 0.000 description 1
- 238000005516 engineering process Methods 0.000 description 1
- -1 etc. Substances 0.000 description 1
- 244000144992 flock Species 0.000 description 1
- 239000010797 grey water Substances 0.000 description 1
- 238000002347 injection Methods 0.000 description 1
- 239000007924 injection Substances 0.000 description 1
- 244000005700 microbiome Species 0.000 description 1
- 239000000203 mixture Substances 0.000 description 1
- 150000007524 organic acids Chemical class 0.000 description 1
- 235000005985 organic acids Nutrition 0.000 description 1
- 238000001556 precipitation Methods 0.000 description 1
- 230000001737 promoting effect Effects 0.000 description 1
- 238000004062 sedimentation Methods 0.000 description 1
- 238000000926 separation method Methods 0.000 description 1
- 239000006228 supernatant Substances 0.000 description 1
Landscapes
- Treatment Of Sludge (AREA)
Abstract
Description
【発明の詳細な説明】
〔産業上の利用分野〕
本発明は、下水等の処理工程において生じる汚泥の脱水
方法およびそれに用いる薬剤に関するものである。DETAILED DESCRIPTION OF THE INVENTION [Field of Industrial Application] The present invention relates to a method for dewatering sludge produced in a treatment process for sewage, etc., and a drug used therein.
都市下水や家庭雑排水等は、有機物の含有量が多いため
、その処理には、好気性微生物に上記有機物を食べさせ
る活性汚泥法が汎用されている。Since urban sewage and domestic gray water contain a large amount of organic matter, the activated sludge method, in which aerobic microorganisms are fed with the organic matter, is widely used for treatment.
上記活性汚泥法によって生じる汚泥の処理は、通常つぎ
のようにしてなされている。すなわち、汚泥が沈澱する
沈澱槽から上澄み液を除去し汚泥のみを消化槽に挿入す
る。この状態では汚泥はしゃぶしゃぶの状態である。こ
の消化槽内において、汚泥の固形分を沈澱?a縮させた
のち脱水機によってさらに汚泥を脱水し、脱水ケーキと
して取り出す。取り出された脱水ケーキは、そのまま投
棄処分されるか焼却処理される。The sludge produced by the above activated sludge method is usually treated as follows. That is, the supernatant liquid is removed from the settling tank where the sludge settles, and only the sludge is inserted into the digestion tank. In this state, the sludge is in a sticky state. Is the solid content of the sludge settled in this digestion tank? After shrinking, the sludge is further dehydrated using a dehydrator and taken out as a dehydrated cake. The removed dehydrated cake is either dumped or incinerated.
上記消化汚泥の脱水処理に際しては、通常、まず槽内に
電解質である無機系凝集剤を投入して汚泥内に浮遊する
コロイド粒子の帯電を中和させることが行われる。これ
によってコロイド粒子同士が凝集して小フロックを形威
する。つぎに槽内に高分子系凝集剤を投入し、上記小フ
ロックを架橋,結合させることによりフロックを戒長さ
せ粗大化させる.このようにして汚泥中の固形分を大フ
ロックにして脱水を促進させている。When dewatering the digested sludge, an inorganic flocculant, which is an electrolyte, is usually first introduced into the tank to neutralize the electrical charge of colloidal particles floating in the sludge. This causes the colloidal particles to aggregate and form small flocs. Next, a polymer flocculant is introduced into the tank to crosslink and bond the small flocs, thereby lengthening and coarsening the flocs. In this way, the solid content in the sludge is turned into large flocs to promote dewatering.
しかしながら、上記のように、無機系凝集剤と高分子系
凝集剤を2段階に分けて投入することは非常に手間であ
り、管理上好ましくない。そこで、両者を同時に槽内に
投入することも考えられるが、両者を同時に共存させる
と、無機系凝集剤によるフロック生戒が高分子系凝集剤
の存在によって妨げられ、高分子系凝集剤によるフロッ
ク戒長が無機系凝集剤の存在で妨げられるため、大フロ
ックが得られず、固一液分離が充分に行われないという
問題がある。したがって、両者の同時投入はできないと
いうのが常識になっている。However, as described above, adding the inorganic flocculant and the polymeric flocculant in two stages is very time-consuming and undesirable from a management standpoint. Therefore, it is possible to introduce both into the tank at the same time, but if both are allowed to coexist at the same time, the presence of the polymeric flocculant will prevent the flocculation caused by the inorganic flocculant, and the flocculation caused by the polymeric flocculant will occur. There is a problem in that large flocs cannot be obtained and solid-liquid separation cannot be performed satisfactorily because the precipitate is hindered by the presence of the inorganic flocculant. Therefore, it is common knowledge that both cannot be used at the same time.
本発明は、このような事情に鑑みなされたもので、汚泥
の脱水処理を行うに際し、無機系凝集剤と高分子系凝集
剤を同時に投入して効果的に処理することのできる脱水
方法およびそれに用いる薬剤の提供をその目的とする.
(問題点を解決するための手段)
上記の目的を達成するため、本発明は、下水の消化汚泥
を脱水するに際し、キトサンおよびキトサン塩類の少な
くとも一方を0.5〜5重量%含有する塩化第二鉄水溶
液からなる薬剤を、汚泥1nfに対し2〜5lの割合で
添加して汚泥中の固体分の脱水を行うようにした汚泥の
脱水方法を第1の要旨とし、下水の消化汚泥を脱水する
ための薬剤であって、キトサンおよびキトサン塩類の少
なくとも一方を0. 5〜5重量%含有する塩化第二鉄
水溶液からなる薬剤を第2の要旨とする。The present invention was made in view of the above circumstances, and provides a dewatering method that can effectively process sludge by simultaneously introducing an inorganic flocculant and a polymer flocculant when dewatering sludge. Its purpose is to provide drugs for use. (Means for Solving the Problems) In order to achieve the above object, the present invention provides a chloride solution containing 0.5 to 5% by weight of at least one of chitosan and chitosan salts when dewatering digested sludge of sewage. The first gist is a sludge dewatering method in which a chemical consisting of diiron aqueous solution is added at a ratio of 2 to 5 liters per 1 nf of sludge to dehydrate the solid content in the sludge, and the sewage digested sludge is dehydrated. A drug for treating at least one of chitosan and chitosan salts at 0. The second gist is a drug consisting of an aqueous ferric chloride solution containing 5 to 5% by weight.
すなわち、本発明者らは、汚泥の脱水処理工程の効率化
を図るために、従来2段階で投入していた無機系凝集剤
と高分子系凝集剤を、一液として使用できないか、との
立場から一連の研究を重ねた。その結果、無機系凝集剤
として塩化第二鉄を用い、高分子系凝集剤としてキトサ
ンおよびキトサン塩類の少なくとも一方を所定の範囲内
で用いるようにすると、両者を配合したー液を用いるだ
けで、優れた凝集効果が得られることを見いだし本発明
に到達した.
つぎに、本発明を詳細に説明する.
本発明に用いる汚泥の凝集促進用薬剤は、塩化第二鉄水
溶液に、キトサンおよびキトサン塩類の少なくとも一方
を含有させた溶液である。In other words, in order to improve the efficiency of the sludge dewatering process, the present inventors wondered if it would be possible to use an inorganic flocculant and a polymer flocculant as a single solution, which had traditionally been introduced in two stages. I conducted a series of studies from my standpoint. As a result, by using ferric chloride as an inorganic flocculant and using at least one of chitosan and chitosan salts as a polymeric flocculant within a predetermined range, it is possible to The present invention was achieved by discovering that an excellent agglomeration effect can be obtained. Next, the present invention will be explained in detail. The sludge flocculation promoting agent used in the present invention is a solution containing at least one of chitosan and chitosan salts in an aqueous ferric chloride solution.
上記塩化第二鉄水溶液としては、塩化第二鉄を35〜4
0重量%(以下「%」と略す)、特に36〜38%含有
する水溶液が好適である.塩化第二鉄の含有量がこの範
囲より多すぎても少なすぎても凝集フロックの或長が不
充分となる傾向がみられるからである.
また、上記塩化第二鉄水溶液に含有させるキトサンは、
カニ.エビ,オキアξ等の甲殻類の外殻から得られるキ
チンをさらに脱アセチル化したもので、下記の一般式で
示すことができる.(以 下 余 白)
上記キトサンとしては、例えば下記の第1表に示すよう
な市販品をあげることができる.(以 下 余 白)
なお、キトサン塩類は、上記キトサンのアξノ基部分が
塩になっているもので、キトサンの塩酸塩.キトサンの
酢酸塩等があげられる。The above ferric chloride aqueous solution contains 35 to 4 ferric chloride.
An aqueous solution containing 0% by weight (hereinafter abbreviated as "%"), particularly 36 to 38%, is suitable. This is because if the ferric chloride content is too high or too low within this range, the flocs tend to become insufficiently long. In addition, the chitosan contained in the ferric chloride aqueous solution is
crab. It is obtained by further deacetylating chitin obtained from the outer shells of crustaceans such as shrimp and Ochia ξ, and can be represented by the general formula below. (Left below) Examples of the above-mentioned chitosan include commercially available products as shown in Table 1 below. (Margin below) Chitosan salts are those in which the ξ group of chitosan is a salt, and is chitosan hydrochloride. Examples include chitosan acetate.
上記キトサンおよびキトサン塩類は、いずれもカチオン
系で、有機酸類に溶解する特性を示す。Both chitosan and chitosan salts are cationic and have the property of being soluble in organic acids.
したがって、前記塩化第二鉄水溶液に、上記キトサン類
を配合し撹拌すると、やや粘稠で褐色の透明な溶液が得
られる。上記キトサン類の配合割合は、前記塩化第二鉄
水溶液に対し、0.5〜5%に設定することが必要であ
る。キトサン類が上記範囲よりも少ないとフロックを威
長させる効果が乏しくなり、逆にキトサン頻が上記の範
囲よりも多いと、塩化第二鉄によるフロック生戒が阻害
されて凝集しない。Therefore, when the above-mentioned chitosan is blended into the above-mentioned ferric chloride aqueous solution and stirred, a slightly viscous, brown, transparent solution is obtained. The blending ratio of the chitosans needs to be set to 0.5 to 5% with respect to the ferric chloride aqueous solution. If the amount of chitosan is less than the above range, the effect of increasing flocs will be poor, and if the amount of chitosan is more than the above range, floc control by ferric chloride will be inhibited and flocculation will not occur.
上記キトサン類が含有された塩化第二鉄水溶液からなる
薬剤を、汚泥1Mに対し、2〜5lの割合で汚泥処理槽
内に投入すると、汚泥内の固体分が大フロックとなり沈
澱する。したがって、これを脱水機にかけると、含水率
の低い脱水ケーキが得られる。なお、上記薬剤の投入量
が、上記範囲よりも少なすぎると凝集沈澱効果が得られ
ず、逆に、上記範囲よりも多くしてもさほど効果が上が
らず経済的でない。When a chemical agent consisting of an aqueous ferric chloride solution containing the chitosans is introduced into a sludge treatment tank at a ratio of 2 to 5 liters per 1M of sludge, the solid content in the sludge becomes large flocs and settles. Therefore, when this is applied to a dehydrator, a dehydrated cake with a low moisture content is obtained. It should be noted that if the amount of the above-mentioned drug added is too small than the above-mentioned range, no coagulation-sedimentation effect will be obtained, and conversely, if the amount of the above-mentioned drug added is too much than the above-mentioned range, the effect will not be so great and it will not be economical.
また、上記薬剤の投入時には、凝集効果を高めるために
、必要に応じて他の凝集沈澱剤や補助剤を併用するよう
にしてもよい。Furthermore, when adding the above-mentioned drug, other coagulation-precipitating agents or auxiliary agents may be used in combination as necessary in order to enhance the coagulation effect.
つぎに、実施例について比較例と併せて説明する。Next, examples will be described together with comparative examples.
実際の下水処理場において、消化汚泥(有機物含有率7
2%、固形分濃度3%)を5ボ/時の1合で供給し、固
形分の凝集沈澱を行った。このとき、凝集剤として下記
の組成のものを用い、下記の条件で処理した。In actual sewage treatment plants, digested sludge (organic content: 7
2%, solid content concentration 3%) was fed at a rate of 5 bottles/hour, and the solid content was coagulated and precipitated. At this time, a flocculant having the following composition was used and the treatment was carried out under the following conditions.
〈凝集剤〉
塩化第二鉄 3B.0重量部水
6 2. O 〃キトサン
1.O〃
供給割合 151/時このようにして
得られた汚泥固形分を、脱水機(ベルトフィルター:ベ
ルト幅1.2m)にかけて脱水し、得られた脱水ケーキ
の含水率を測定したところ、73%であった。<Flocculant> Ferric chloride 3B. 0 parts by weight water
6 2. O Chitosan
1. O〃 Supply rate 151/hour The sludge solid content thus obtained was dehydrated using a dehydrator (belt filter: belt width 1.2 m), and the moisture content of the resulting dehydrated cake was measured and found to be 73%. Met.
〔比較例1〕
上記実施例と同様にして汚泥の凝集沈澱を行った.ただ
し、凝集剤として下記のA,82種類のものを順次供給
した。[Comparative Example 1] Sludge was coagulated and sedimented in the same manner as in the above example. However, the following 82 kinds of flocculants A were sequentially supplied as flocculants.
く凝集剤A〉
塩化第二鉄 38.0重量部水
6 2. 0 〃く凝集剤B〉
アニオン系高分子系凝集剤 0.1重量部凝集剤Bの供
給割合 1501/時このようにして得られた汚
泥固形分を、上記実施例と同様にして脱水し、得られた
脱水ケーキの含水率を測定したところ、76%であった
。Flocculant A> Ferric chloride 38.0 parts by weight water
6 2. 0 〃Flocculant B〉 Anionic polymer flocculant 0.1 parts by weight Feed rate of flocculant B 1501/hour The sludge solid content thus obtained was dehydrated in the same manner as in the above example, The moisture content of the obtained dehydrated cake was measured and found to be 76%.
このように、上記実施例によれば、一段階の凝集剤の供
給のみで、従来の二段階薬液供給によつて得られるもの
よりも3%も低い含水率を達戒している。この差は、実
際の下水処理場等において何千トン,何万トン単位の大
量の汚泥を扱う場合に、非常に大きな差となり、有利で
ある.〔実施例2.3、比較例2.3〕
下記の第2表に示すようにキトサンの配合割合を変えた
。それ以外は上記実施例と同様にして汚泥の脱水処理を
行い、得られた脱水ケーキの含水率を測定した。その結
果を下記の第2表に併せて示す。As described above, according to the above embodiment, a water content that is 3% lower than that obtained by the conventional two-stage chemical solution supply can be achieved by only one-stage flocculant supply. This difference is very large and advantageous when dealing with large amounts of sludge in the thousands or tens of thousands of tons at actual sewage treatment plants. [Example 2.3, Comparative Example 2.3] The blending ratio of chitosan was changed as shown in Table 2 below. Other than that, the sludge was dehydrated in the same manner as in the above example, and the water content of the obtained dehydrated cake was measured. The results are also shown in Table 2 below.
〔実施例4〜8〕
塩化第二鉄の含有量が凝集効果に与える影響について調
べるために、塩化第二鉄の量を下記の第3表に示すよう
に変えた。それ以外は上記実施例lと同様にして汚泥の
脱水処理を行い、得られた脱水ケーキの含水率を測定し
た。その結果を下記の第3表に併せて示す。[Examples 4 to 8] In order to investigate the influence of the content of ferric chloride on the flocculation effect, the amount of ferric chloride was varied as shown in Table 3 below. Otherwise, the sludge was dehydrated in the same manner as in Example 1 above, and the water content of the resulting dehydrated cake was measured. The results are also shown in Table 3 below.
上記の結果から、キトサンの量が適正範囲から外れた比
較例品は、脱水ケーキの含水率が高くなっており、脱水
効果に乏しいことがわかる。From the above results, it can be seen that in the comparative example product in which the amount of chitosan was outside the appropriate range, the water content of the dehydrated cake was high and the dehydration effect was poor.
上記の結果から、塩化第二鉄の含有量は、35〜40%
の範囲内で優れた凝集効果があることがわかる.
〔発明の効果〕
以上のように、本発明によれば、無機系凝集剤と高分子
系凝集剤を別々に供給して段階的にフロックを生或・威
長させて凝集沈澱させる必要がなく、一段階で効果的に
大きなフロックをつぐることかできる。したがって、脱
水工程における薬剤投入が1回で済み、その管理が非常
に容易となる。しかも、従来よりも効果的な凝集沈澱が
なされるため、脱水後の脱水ケーキの含水率も低くなる
という効果を奏する。From the above results, the content of ferric chloride is 35-40%
It can be seen that there is an excellent agglomeration effect within the range of . [Effects of the Invention] As described above, according to the present invention, there is no need to supply an inorganic flocculant and a polymeric flocculant separately to produce and grow flocs in stages to coagulate and precipitate them. , you can effectively weave large flocks in one step. Therefore, the chemical injection in the dehydration process only needs to be done once, and its management becomes very easy. Furthermore, since coagulation and precipitation are more effective than in the past, the water content of the dehydrated cake after dehydration is also lowered.
Claims (3)
びキトサン塩類の少なくとも一方を0.5〜5重量%含
有する塩化第二鉄水溶液からなる薬剤を、汚泥1m^3
に対し2〜5lの割合で添加して汚泥中の固体分の脱水
を行うようにしたことを特徴とする汚泥の脱水方法。(1) When dewatering digested sewage sludge, a chemical consisting of a ferric chloride aqueous solution containing 0.5 to 5% by weight of at least one of chitosan and chitosan salts is added to 1 m^3 of the sludge.
1. A method for dewatering sludge, characterized in that the solid content in the sludge is dehydrated by adding 2 to 5 liters of water to the sludge.
キトサンおよびキトサン塩類の少なくとも一方を0.5
〜5重量%含有する塩化第二鉄水溶液からなることを特
徴とする薬剤。(2) A drug for dehydrating digested sludge from sewage,
At least one of chitosan and chitosan salts at 0.5
A drug comprising an aqueous solution of ferric chloride containing ~5% by weight.
量%含有するものである請求項(2)記載の薬剤。(3) The drug according to claim (2), wherein the ferric chloride aqueous solution contains 35 to 40% by weight of ferric chloride.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP1153058A JPH0316700A (en) | 1989-06-15 | 1989-06-15 | Method for dehydrating sludge and chemicals used therefor |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP1153058A JPH0316700A (en) | 1989-06-15 | 1989-06-15 | Method for dehydrating sludge and chemicals used therefor |
Publications (1)
Publication Number | Publication Date |
---|---|
JPH0316700A true JPH0316700A (en) | 1991-01-24 |
Family
ID=15554062
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP1153058A Pending JPH0316700A (en) | 1989-06-15 | 1989-06-15 | Method for dehydrating sludge and chemicals used therefor |
Country Status (1)
Country | Link |
---|---|
JP (1) | JPH0316700A (en) |
Cited By (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US5393435A (en) * | 1993-09-17 | 1995-02-28 | Vanson L.P. | Removal of organic contaminants from aqueous media |
JP2008179728A (en) * | 2007-01-25 | 2008-08-07 | Sumitomo Rubber Ind Ltd | Rubber composition and tire using the same |
CN103880265A (en) * | 2012-12-21 | 2014-06-25 | 湖南清和污泥资源利用有限公司 | Sludge processing method |
Citations (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS5335866A (en) * | 1976-09-16 | 1978-04-03 | Hitachi Ltd | Automobile automatic speed change gear control system |
JPS5982911A (en) * | 1982-11-01 | 1984-05-14 | Kurita Water Ind Ltd | Composition for flocculating agent |
-
1989
- 1989-06-15 JP JP1153058A patent/JPH0316700A/en active Pending
Patent Citations (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS5335866A (en) * | 1976-09-16 | 1978-04-03 | Hitachi Ltd | Automobile automatic speed change gear control system |
JPS5982911A (en) * | 1982-11-01 | 1984-05-14 | Kurita Water Ind Ltd | Composition for flocculating agent |
Cited By (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US5393435A (en) * | 1993-09-17 | 1995-02-28 | Vanson L.P. | Removal of organic contaminants from aqueous media |
JP2008179728A (en) * | 2007-01-25 | 2008-08-07 | Sumitomo Rubber Ind Ltd | Rubber composition and tire using the same |
CN103880265A (en) * | 2012-12-21 | 2014-06-25 | 湖南清和污泥资源利用有限公司 | Sludge processing method |
CN103880265B (en) * | 2012-12-21 | 2017-03-15 | 湖南清和环保技术有限公司 | A kind of method for processing sludge |
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