CN102276039A - Method for removing phosphorus from phosphorus-rich water body by natural mineral mixture - Google Patents

Method for removing phosphorus from phosphorus-rich water body by natural mineral mixture Download PDF

Info

Publication number
CN102276039A
CN102276039A CN2011101305164A CN201110130516A CN102276039A CN 102276039 A CN102276039 A CN 102276039A CN 2011101305164 A CN2011101305164 A CN 2011101305164A CN 201110130516 A CN201110130516 A CN 201110130516A CN 102276039 A CN102276039 A CN 102276039A
Authority
CN
China
Prior art keywords
phosphorus
solution
phosphorus concentration
anhydrite
dephosphorization
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
CN2011101305164A
Other languages
Chinese (zh)
Inventor
张宏
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.)
Guilin University of Technology
Original Assignee
Guilin University of Technology
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 Guilin University of Technology filed Critical Guilin University of Technology
Priority to CN2011101305164A priority Critical patent/CN102276039A/en
Publication of CN102276039A publication Critical patent/CN102276039A/en
Pending legal-status Critical Current

Links

Landscapes

  • Removal Of Specific Substances (AREA)

Abstract

The invention discloses a method for removing phosphorus from a phosphorus-rich water body by a natural mineral mixture. Calcite and anhydrite powders with the particle size being 150-800 meshes are respectively weighed and mixed according to the mass ratio of 4:1-14:1; in a solution at the initial phosphorus concentration of 1000mg/L-2mg/L, the mixture reacts for 1-12 hours at the temperature of 15-30 DEG C and the effective dephosphorization amount corresponding to 1g of gypsum in the mixed mineral ranges from (0.1*CP)mg to (0.9*CP)mg; after the dephosphorization effect by the use of the mixed mineral is low, the anhydrite mineral powder is added and then the effective dephosphorization amount corresponding to 1g of gypsum ranges from (0.15*CP)mg to (2*CP)mg, wherein CP is the value of the initial phosphorus concentration (mg/L) of the solution. The method provided by the invention can be applied to remove and recover phosphorus from urban life sewage, industrial wastewater, rural scattered life sewage and phosphorus-rich water bodies such as an eutrophic lake water body, large-scale, middle-sized and pint-sized eutrophic landscape water bodies and the like.

Description

The natural mineral mixture is to the method for dephosphorization for rich-phosphorus water body
Technical field
The invention belongs to the water pollution control field, the specified proportion mixture that refers in particular to natural mineral dephosphorization and reclaiming in the process of phosphorus in rich-phosphorus water body or sewage, the quantitative Application method of Shi Yonging repeatedly.
Background technology
Phosphorus is the main inducible factor of body eutrophication, so in the process of the serious day by day global eutrophication problem of reply, at first pay attention to the control to phosphorus.
In developed country, the processing of phosphor in sewage is paid much attention to, especially pay attention in trade effluent and domestic sewage treating process recycling to phosphorus; And developed corresponding recovery technology--with the inorganic mineral magnesium ammonium phosphate (MgNH of phosphorus 4PO 46H 2O is commonly called as struvite or MAP) and the calcium phosphate technology be main.For example, MAP crystallization retrieving arrangement has been installed by gondola Treviso sewage work on sludge dewatering supernatant liquor circuit, and the rate of recovery is 54%, and this technology is in calendar year 2001 putting into production property operation; Britain Slough sewage work handles the sludge dewatering supernatant liquor with the MAP settler, and goes into operation in 2002, is 80% to the rate of recovery of soluble phosphate; Holland Geestmerambacht Sewage Plant adopts the Crystalactor technology to reclaim calcium phosphate.
At present, there is following problem in dephosphorization (recovery phosphorus) method of developed country's employing:
1. magnesium ammonium phosphate of Cai Yonging and calcium phosphate mineral recovery method be mainly used in in trade effluent and the city domestic sewage dephosphorization process to the recovery of phosphorus, but can't remove and recycle the phosphorus in the occurring in nature eutrophication water (as rural area dispersant type domestic wastewater, scenic spot rich-phosphorus water body).
2. finish by adding chemical reagent such as MgCl with the form dephosphorization (recovery phosphorus) of magnesium ammonium phosphate, its shortcoming is that running cost is very high, and requires operation (this is impossible in the nature water body) under higher pH (pH>9) background.So application prospect remains further to be studied.
3. the form dephosphorization (recovery phosphorus) with calcium phosphate is by adding Na (OH), Ca (OH) 2Finish Deng chemical reagent, not only cost is higher, also exists operational conditions to require harsh problem simultaneously, is difficult to carry out the large-scale production operation of nature rich-phosphorus water body.
4. aforesaid method is not also realized real quantification processing, and the maturity of its technology awaits further exploitation.
In China, many scholars study the recycle of dephosphorization and phosphorus from different angles, as Wang Huizhen, and Wang Shaogui. reclaim phosphorus research with the calcium phosphate salt form from Sewage Plant. Chinese water supply and drainage, 2006,122 (9): 93~96; Sun Boya, Chen Hongbin, the progress that sewage disposal phosphorus reclaims. the Sichuan environment, 2007,26 (1): 90~94, but majority still rests on breadboard conceptual phase, and lack the experimental program that promotion prospect is arranged and the measure of system.
Present patent application is not only on the basis of a large amount of experimental datas, revises according to a large amount of pilot-scale experiment simultaneously, and concrete technology possesses the operability of practical application fully; And carried out more deep research, but not only the reality range of application is wider, and further reduced cost.
Summary of the invention
The purpose of this invention is to provide a kind of natural mineral mixture to the dephosphorization of rich-phosphorus water body or sewage and the method for recovery phosphorus, and dephosphorization (recovery phosphorus) efficient height, requiring of operational conditions is low, cost is low, not only can be used for city domestic sewage and trade effluent dephosphorization, reclaim phosphorus, can also be applied to the rich-phosphorus water bodies such as eutrophic landscape water body of rural area dispersant type domestic wastewater and large, medium and small type dephosphorization, reclaim phosphorus.
Concrete steps of the present invention are:
Step 1:
Take by weighing calcite mineral crystal and anhydrite mineral crystal powder respectively, particle diameter mixes by 4: 1~14: 1 mass ratioes between 150~800 orders, insert in the Erlenmeyer flask, then, adding initial phosphorus concentration is the solution 100mL of 1000mg/L~2mg/L, between pH regulator to 5~10; Put into constant temperature oscillator, design temperature is between 15 ℃~30 ℃, and question response was got its supernatant liquor after 1~12 hour, with the phosphorus concentration of this supernatant liquor of ammonium molybdate spectrophotometry; Then, supernatant liquor in the Erlenmeyer flask is removed, the remaining mixed mineral powder oven dry in the Erlenmeyer flask, adding initial phosphorus concentration again is the solution 100mL of 1000mg/L~2mg/L, put into constant temperature oscillator, repetitive operation under these conditions, until its remove phosphorus and reclaim effect of phosphorus when low till; The lower standard of effect of removing phosphorus and reclaiming phosphorus is: at initial phosphorus concentration is dephosphorizing rate≤95% in 1000mg/L~100mg/L solution, at initial phosphorus concentration is dephosphorizing rate≤90% in 100mg/L~20mg/L solution, at initial phosphorus concentration is dephosphorizing rate≤80% in 20mg/L~10mg/L solution, at initial phosphorus concentration is dephosphorizing rate≤75% in 10mg/L~2mg/L solution, dephosphorizing rate≤70% in initial phosphorus concentration≤2mg/L solution;
Step 2:
With the remaining mixed mineral powder oven dry that step () obtains, adding initial phosphorus concentration is the solution 100mL of 1000mg/L~2mg/L, and between pH regulator to 5~10, adding 150~800 purpose anhydrite mineral crystal powder again is that gypsum adds for the first time; Put into constant temperature oscillator, repetitive operation under these conditions, when effect of its removal phosphorus and recovery phosphorus is hanged down, more for the second time, for the third time ... the 200th adding anhydrite mineral crystal powder.
The result shows: the scope of effective dephosphorization amount of every 1g gypsum correspondence is at (0.1*C in the mixed mineral P) mg~(0.9*C P) mg (C PNumerical value for the initial phosphorus concentration (mg/L) of solution).Remove the phosphorus effect than after low at mixed mineral, add the anhydrite mineral dust, at this moment, effective dephosphorization amount of every 1g gypsum correspondence is at (0.15*C P) mg~(2*C P) (C between the mg PNumerical value for the initial phosphorus concentration (mg/L) of solution).
Beneficial effect:
(1) effect of this method dephosphorization can reach 89~99%; The phosphorus balance concentration of handling the back water body is about 0.1-0.4mg/L.
(2) determined the injected volume of mixed mineral and the relation of effective dephosphorization total amount, made the dephosphorization realization quantification of rich-phosphorus water body is controlled.
(3) this method can make and corresponding water body trend neutralisation (pH value convergence about 7.5) development make water body optimization, can not form secondary pollution again, and is easy to use.
(4) advantage compared with external existing technology of the present invention is: the natural mineral with cheapness carries out mixing match, does not need to add any chemical agent.It not only can be used for the dephosphorization of city domestic sewage, trade effluent, can also be applied to dephosphorization, the recovery phosphorus of the rich-phosphorus water bodies such as eutrophic landscape water body of rural area dispersant type domestic wastewater and large, medium and small type.
(5) cost only is equivalent to about 1/30 of existing phosphorus recovery technology abroad.The dephosphorization cost that initial phosphorus concentration per ton is the 10mg/L water body is a 0.17-0.25 unit; The cost that then reclaims calcium phosphate is about 2500-3800 unit/ton (RMB), and the cost that external Crystalactor technology reclaims calcium phosphate then is 76000-80000 unit/ton (RMB).
Embodiment
Finish by two steps:
Step 1
Embodiment 1.
The ratio of getting is that (particle diameter of calcite is 800 orders for the mixed mineral powder 10g of 4: 1 (mass ratio of calcite/anhydrite), the particle diameter of gypsum is 800 orders), the capacity of inserting is in the 200mL Erlenmeyer flask, adding initial phosphorus concentration is the solution 100mL of 1000mg/L, and pH regulator to 7 is put into constant temperature oscillator, setting rotating speed is 150 commentaries on classics/min, temperature is 30 ℃, reacts after 12 hours, gets its supernatant liquor test.Then, the supernatant liquor in the Erlenmeyer flask is removed, the remaining mixed mineral powder oven dry in the Erlenmeyer flask, adding initial phosphorus concentration again is the solution 100mL of 1000mg/L, repetitive operation under these conditions, when the effect of its dephosphorization (recovery phosphorus) is low till.Last effective dephosphorization total amount is 298.75mg, then effective dephosphorization amount of 1g gypsum correspondence be 149.27mg (table 1, No.1).
Embodiment 2.
The ratio of getting is that (particle diameter of calcite is 800 orders for the mixed mineral powder 10g of 9: 1 (mass ratio of calcite/anhydrite), the particle diameter of gypsum is 500 orders), the capacity of inserting is in the 200mL Erlenmeyer flask, adding initial phosphorus concentration is the solution 100mL of 100mg/L, and pH regulator to 6 is put into constant temperature oscillator, setting rotating speed is 150 commentaries on classics/min, temperature is 25 ℃, reacts after 10 hours, gets its supernatant liquor test.Then, the supernatant liquor in the Erlenmeyer flask is removed, the remaining mixed mineral powder oven dry in the Erlenmeyer flask, adding initial phosphorus concentration again is the solution 100mL of 100mg/L, repetitive operation under these conditions, when the effect of its dephosphorization (recovery phosphorus) is low till.Last effective dephosphorization total amount is 29.82mg, then effective dephosphorization amount of 1g gypsum correspondence be 29.82mg (table 1, No.2).
Embodiment 3.
The ratio of getting is that (particle diameter of calcite is 800 orders for the mixed mineral powder 15g of 14: 1 (mass ratio of calcite/anhydrite), the particle diameter of gypsum is 600 orders), the capacity of inserting is in the 200mL Erlenmeyer flask, adding initial phosphorus concentration is the solution 100mL of 50mg/L, and pH regulator to 6 is put into constant temperature oscillator, setting rotating speed is 150 commentaries on classics/min, temperature is 25 ℃, reacts after 10 hours, gets its supernatant liquor test.Then, the supernatant liquor in the Erlenmeyer flask is removed, the remaining mixed mineral powder oven dry in the Erlenmeyer flask, adding initial phosphorus concentration again is the solution 100mL of 50mg/L, repetitive operation under these conditions, when the effect of its dephosphorization (recovery phosphorus) is low till.Last effective dephosphorization total amount is 19.76mg, then effective dephosphorization amount of 1g gypsum correspondence be 19.76mg (table 1, No.3).
Embodiment 4.
The ratio of getting is that (particle diameter of calcite is 150 orders for the mixed mineral powder 6g of 14: 1 (mass ratio of calcite/anhydrite), the particle diameter of gypsum is 150 orders), the capacity of inserting is in the 200mL Erlenmeyer flask, adding initial phosphorus concentration is the solution 100mL of 20mg/L, and pH regulator to 5 is put into constant temperature oscillator, setting rotating speed is 150 commentaries on classics/min, temperature is 30 ℃, reacts after 10 hours, gets its supernatant liquor test.Then, the supernatant liquor in the Erlenmeyer flask is removed, the remaining mixed mineral powder oven dry in the Erlenmeyer flask, adding initial phosphorus concentration again is the solution 100mL of 20mg/L, repetitive operation under these conditions, when the effect of its dephosphorization (recovery phosphorus) is low till.Last effective dephosphorization total amount is 1.718mg, then effective dephosphorization amount of 1g gypsum correspondence be 4.29mg (table 1, No.4).
Embodiment 5.
The ratio of getting is that (particle diameter of calcite is 800 orders for the mixed mineral powder 5g of 4: 1 (mass ratio of calcite/anhydrite), the particle diameter of gypsum is 800 orders), the capacity of inserting is in the 200mL Erlenmeyer flask, and adding initial phosphorus concentration is the solution 100mL of 15mg/L, pH regulator to 7; Put into constant temperature oscillator, setting rotating speed is 150 commentaries on classics/min, and temperature is 30 ℃, reacts after 4 hours, gets its supernatant liquor test.Then, the supernatant liquor in the Erlenmeyer flask is removed, the remaining mixed mineral powder oven dry in the Erlenmeyer flask, adding initial phosphorus concentration again is the solution 100mL of 15mg/L, repetitive operation under these conditions, when the effect of its dephosphorization (recovery phosphorus) is low till.Last effective dephosphorization total amount is 5.563mg, then effective dephosphorization amount of 1g gypsum correspondence be 5.56mg (table 1, No.5).
Embodiment 6.
The ratio of getting is that (particle diameter of calcite is 250 orders for the mixed mineral powder 4g of 9: 1 (mass ratio of calcite/anhydrite), the particle diameter of gypsum is 800 orders), the capacity of inserting is in the 200mL Erlenmeyer flask, and adding initial phosphorus concentration is the solution 100mL of 10mg/L, pH regulator to 10; Put into constant temperature oscillator, setting rotating speed is 150 commentaries on classics/min, and temperature is 30 ℃, reacts after 8 hours, gets its supernatant liquor test.Then, the supernatant liquor in the Erlenmeyer flask is removed, the remaining mixed mineral powder oven dry in the Erlenmeyer flask, adding initial phosphorus concentration again is the solution 100mL of 10mg/L, repetitive operation under these conditions, when the effect of its dephosphorization (recovery phosphorus) is low till.Last effective dephosphorization total amount is 1.903mg, then effective dephosphorization amount of 1g gypsum correspondence be 4.76mg (table 1, No.6).
Embodiment 7.
The ratio of getting is that (particle diameter of calcite is 300 orders for the mixed mineral powder 4g of 4: 1 (mass ratio of calcite/anhydrite), the particle diameter of gypsum is 500 orders), the capacity of inserting is in the 200mL Erlenmeyer flask, and adding initial phosphorus concentration is the solution 100mL of 8mg/L, pH regulator to 7.5; Put into constant temperature oscillator, setting rotating speed is 150 commentaries on classics/min, and temperature is 25 ℃, reacts after 10 hours, gets its supernatant liquor test.Then, the supernatant liquor in the Erlenmeyer flask is removed, the remaining mixed mineral powder oven dry in the Erlenmeyer flask, adding initial phosphorus concentration again is the solution 100mL of 8mg/L, repetitive operation under these conditions, when the effect of its dephosphorization (recovery phosphorus) is low till.Last effective dephosphorization total amount is 3.010mg, then effective dephosphorization amount of 1g gypsum correspondence be 3.76mg (table 1, No.7).
Embodiment 8.
The ratio of getting is that (particle diameter of calcite is 700 orders for the mixed mineral powder 4g of 4: 1 (mass ratio of calcite/anhydrite), the particle diameter of gypsum is 600 orders), the capacity of inserting is in the 200mL Erlenmeyer flask, and adding initial phosphorus concentration is the solution 100mL of 6mg/L, pH regulator to 6; Put into constant temperature oscillator, setting rotating speed is 150 commentaries on classics/min, and temperature is 15 ℃, reacts after 10 hours, gets its supernatant liquor test.Then, the supernatant liquor in the Erlenmeyer flask is removed, the remaining mixed mineral powder oven dry in the Erlenmeyer flask, adding initial phosphorus concentration again is the solution 100mL of 6mg/L, repetitive operation under these conditions, when the effect of its dephosphorization (recovery phosphorus) is low till.Last effective dephosphorization total amount is 1.643mg, then effective dephosphorization amount of 1g gypsum correspondence be 2.05mg (table 1, No.8).
Embodiment 9.
The ratio of getting is that (particle diameter of calcite is 800 orders for the mixed mineral powder 5g of 4: 1 (mass ratio of calcite/anhydrite), the particle diameter of gypsum is 600 orders), the capacity of inserting is in the 200mL Erlenmeyer flask, and adding initial phosphorus concentration is the solution 100mL of 4mg/L, pH regulator to 7; Put into constant temperature oscillator, setting rotating speed is 150 commentaries on classics/min, and temperature is 25 ℃, reacts after 10 hours, gets its supernatant liquor test.Then, the supernatant liquor in the Erlenmeyer flask is removed, the remaining mixed mineral powder oven dry in the Erlenmeyer flask, adding initial phosphorus concentration again is the solution 100mL of 4mg/L, repetitive operation under these conditions, when the effect of its dephosphorization (recovery phosphorus) is low till.Last effective dephosphorization total amount is 2.616mg, then effective dephosphorization amount of 1g gypsum correspondence be 2.62 (table 1, No.9).
Embodiment 10.
The ratio of getting is that (particle diameter of calcite is 600 orders for the mixed mineral powder 5g of 4: 1 (mass ratio of calcite/anhydrite), the particle diameter of gypsum is 500 orders), the capacity of inserting is in the 200mL Erlenmeyer flask, and adding initial phosphorus concentration is the solution 100mL of 2mg/L, pH regulator to 10; Put into constant temperature oscillator, setting rotating speed is 150 commentaries on classics/min, and temperature is 20 ℃, reacts after 12 hours, gets its supernatant liquor test.Then, the supernatant liquor in the Erlenmeyer flask is removed, the remaining mixed mineral powder oven dry in the Erlenmeyer flask, adding initial phosphorus concentration again is the solution 100mL of 2mg/L, repetitive operation under these conditions, when the effect of its dephosphorization (recovery phosphorus) is low till.Last effective dephosphorization total amount is 0.546mg, then effective dephosphorization amount of 1g gypsum correspondence be 0.55mg (table 1, No.10).
10 embodiment explanations in the step 1, be respectively in the solution of 1000mg/L~2mg/L at initial phosphorus concentration, the mineral particle diameter is that the mass ratio of 150~800 orders, calcite/anhydrite is 4: 1~14: 1, pH regulator 5~10, under 15 ℃~30 ℃ of the temperature, the condition in 4~12 hours reaction times, effective dephosphorization total amount of every 1g gypsum is (0.1*C in the mixed mineral P) mg~(0.9*C P) mg (C PNumerical value for the initial phosphorus concentration (mg/L) of solution).
Step 2
Embodiment 11.
Remove the lower remaining mixed mineral powder oven dry of phosphorus (recovery phosphorus) effect in the Erlenmeyer flask with embodiment 1, adding initial phosphorus concentration again is the solution 100mL of 1000mg/L, add 800 purpose anhydrite mineral crystal powder 2g (gypsum adds for the first time) then, pH regulator to 7; Rotating speed is 150 commentaries on classics/min, temperature is 30 ℃, reacted 10 hours, repetitive operation under this condition, when its effect of removing phosphorus (recovery phosphorus) is hanged down, for the second time add 800 purpose anhydrite mineral crystal powder 2g again, add 800 purpose anhydrite mineral crystal powder 2g for the third time ... the 150th adding 800 purpose anhydrite mineral crystal powder 2g.So, the effective dephosphorization amount that adds for the first time anhydrite is 394.77mg, the effective dephosphorization amount that adds for the second time anhydrite is 297.709mg, and the effective dephosphorization amount that adds anhydrite for the third time is that effective dephosphorization amount of the 150th adding of 398.823mg...... anhydrite is 298.948mg; Then for the first time, for the second time, for the third time ... effective dephosphorization amount of the 150th every 1g gypsum is 197.39,148.85,199.41, and 149.47mg (table 1, No.12).
Embodiment 12.
Remove the lower remaining mixed mineral powder oven dry of phosphorus (recovery phosphorus) effect in the Erlenmeyer flask with embodiment 6, adding initial phosphorus concentration again is the solution 100mL of 10mg/L, add 200 purpose anhydrite mineral crystal powder 0.4g (gypsum adds for the first time) then, pH regulator to 10; Rotating speed is 150 commentaries on classics/min, temperature is 30 ℃, reacted 8 hours, repetitive operation under this condition, when its effect of removing phosphorus (recovery phosphorus) is hanged down, for the second time add 200 purpose anhydrite mineral crystal powder 0.4g again, add 200 purpose anhydrite mineral crystal powder 0.3g for the third time ... the 80th adding 200 purpose anhydrite mineral crystal powder 0.3g.So, the effective dephosphorization amount that adds for the first time anhydrite is 2.857mg, the effective dephosphorization amount that adds for the second time 200 purpose anhydrite is 1.914mg, and the effective dephosphorization amount that adds anhydrite for the third time is that effective dephosphorization amount of the 80th adding of 1.909mg...... anhydrite is 2.700mg; Then for the first time, for the second time, for the third time ... effective dephosphorization amount of the 80th every 1g gypsum is 7.14,4.79,6.36, and 9.00mg (table 1, No.12).
Embodiment 13.
Remove the lower remaining mixed mineral powder oven dry of phosphorus (recovery phosphorus) effect in the Erlenmeyer flask with embodiment 8, adding initial phosphorus concentration again is the solution 100mL of 6mg/L, add 600 purpose anhydrite mineral crystal powder 0.4g (gypsum adds for the first time) then, pH regulator to 7; Rotating speed is 150 commentaries on classics/min, temperature is 25 ℃, reacted 10 hours, repetitive operation under this condition, when its effect of removing phosphorus (recovery phosphorus) is hanged down, for the second time add 600 purpose anhydrite mineral crystal powder 0.4g again, add 600 purpose anhydrite mineral crystal powder 0.3g for the third time ... the 200th adding 600 purpose anhydrite mineral crystal powder 0.3g.So, the effective dephosphorization amount that adds for the first time anhydrite is 1.726mg, the effective dephosphorization amount that adds for the second time anhydrite is 1.149mg, and the effective dephosphorization amount that adds anhydrite for the third time is 1.134mg ... effective dephosphorization amount of the 200th adding anhydrite is 1.142mg; Then for the first time, for the second time, for the third time ... effective dephosphorization amount of every 1g gypsum of the 200th time is 4.23,2.87,3.78, and 3.81mg (table 1, No.13).
Embodiment 14.
Remove the lower remaining mixed mineral powder oven dry of phosphorus (recovery phosphorus) effect in the Erlenmeyer flask with embodiment 10, adding initial phosphorus concentration again is the solution 100mL of 2mg/L, add 400 purpose anhydrite mineral crystal powder 0.6g (gypsum adds for the first time) then, pH regulator to 6; Rotating speed is 150 commentaries on classics/min, temperature is 20 ℃, reacted 12 hours, repetitive operation under this condition, when its effect of removing phosphorus (recovery phosphorus) is hanged down, for the second time add 400 purpose anhydrite mineral crystal powder 0.6g again, add 400 purpose anhydrite mineral crystal powder 0.6g for the third time ... the 200th adding 400 purpose anhydrite mineral crystal powder 0.6g.So, the effective dephosphorization amount that adds gypsum for the first time is 0.489mg, and the effective dephosphorization amount that adds gypsum for the second time is 0.483mg, and effective dephosphorization amount for the third time is that effective dephosphorization amount of the 99th adding of 0.463mg...... anhydrite is 0.486mg; Then for the first time, for the second time, for the third time ... effective dephosphorization amount of every 1g gypsum of the 99th correspondence be 0.82,0.81,0.77,0.81 (table 1, No.14).
4 embodiment of step 2 show that the mixed mineral in the step 1 adds quantitative anhydrite after dephosphorization (recovery phosphorus) effect is low, just can continue dephosphorization; At this moment, effective dephosphorization amount of every 1g anhydrite correspondence is at (0.15*C P) mg~(2*C P) (C between the mg PNumerical value for the initial phosphorus concentration (mg/L) of solution).
The main test data of experiment table look-up of table 1
Figure BSA00000499610200071
Figure BSA00000499610200081
Figure BSA00000499610200101
1) with the method for calculation of anhydrite dependency: the effective anhydrite usage quantity in dephosphorization total amount (∑ p)/experiment.
Annotate: the data that have * are disallowable when calculating the available phosphorus total amount, the standard of rejecting is: at initial phosphorus concentration is dephosphorizing rate≤95% in 1000mg/L~100mg/L solution, at initial phosphorus concentration is dephosphorizing rate≤90% in 100mg/L~20mg/L solution, at initial phosphorus concentration is dephosphorizing rate≤80% in 20mg/L~10mg/L solution, at initial phosphorus concentration is dephosphorizing rate≤75% in 10mg/L~2mg/L solution, dephosphorizing rate≤70% in initial phosphorus concentration≤2mg/L solution).

Claims (1)

1. a natural mineral mixture is characterized in that to the method for dephosphorization for rich-phosphorus water body concrete steps are:
Step 1:
Take by weighing calcite mineral crystal and anhydrite mineral crystal powder respectively, particle diameter mixes by 4: 1~14: 1 mass ratioes between 150~800 orders, insert in the Erlenmeyer flask, then, adding initial phosphorus concentration is the solution 100mL of 1000mg/L~2mg/L, between pH regulator to 5~10; Put into constant temperature oscillator, design temperature is between 15 ℃~30 ℃, and question response was got its supernatant liquor after 1~12 hour, with the phosphorus concentration of this supernatant liquor of ammonium molybdate spectrophotometry; Then, supernatant liquor in the Erlenmeyer flask is removed, the remaining mixed mineral powder oven dry in the Erlenmeyer flask, adding initial phosphorus concentration again is the solution 100mL of 1000mg/L~2mg/L, put into constant temperature oscillator, repetitive operation under these conditions, until its remove phosphorus and reclaim effect of phosphorus when low till; The lower standard of effect of removing phosphorus and reclaiming phosphorus is: at initial phosphorus concentration is dephosphorizing rate≤95% in 1000mg/L~100mg/L solution, at initial phosphorus concentration is dephosphorizing rate≤90% in 100mg/L~20mg/L solution, at initial phosphorus concentration is dephosphorizing rate≤80% in 20mg/L~10mg/L solution, at initial phosphorus concentration is dephosphorizing rate≤75% in 10mg/L~2mg/L solution, dephosphorizing rate≤70% in initial phosphorus concentration≤2mg/L solution;
Step 2:
With the remaining mixed mineral powder oven dry that step () obtains, adding initial phosphorus concentration is the solution 100mL of 1000mg/L~2mg/L, and between pH regulator to 5~10, adding 150~800 purpose anhydrite mineral crystal powder again is that gypsum adds for the first time; Put into constant temperature oscillator, repetitive operation under these conditions, when effect of its removal phosphorus and recovery phosphorus is hanged down, more for the second time, for the third time ... the 200th adding anhydrite mineral crystal powder.
CN2011101305164A 2011-05-17 2011-05-17 Method for removing phosphorus from phosphorus-rich water body by natural mineral mixture Pending CN102276039A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN2011101305164A CN102276039A (en) 2011-05-17 2011-05-17 Method for removing phosphorus from phosphorus-rich water body by natural mineral mixture

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN2011101305164A CN102276039A (en) 2011-05-17 2011-05-17 Method for removing phosphorus from phosphorus-rich water body by natural mineral mixture

Publications (1)

Publication Number Publication Date
CN102276039A true CN102276039A (en) 2011-12-14

Family

ID=45101841

Family Applications (1)

Application Number Title Priority Date Filing Date
CN2011101305164A Pending CN102276039A (en) 2011-05-17 2011-05-17 Method for removing phosphorus from phosphorus-rich water body by natural mineral mixture

Country Status (1)

Country Link
CN (1) CN102276039A (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN110498496A (en) * 2018-05-16 2019-11-26 广西机电工业学校 Technique for applying of the natural minerals to rich-phosphorus water body or sewage dephosphorization and recycling phosphorus
CN110894095A (en) * 2018-05-15 2020-03-20 广西机电工业学校 Quantitative application process of natural minerals for removing phosphorus from phosphorus-rich water body

Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1333024A (en) * 2000-07-06 2002-01-30 佳木斯医学院制药厂 Injection for mammary sland recovery
CN101333024A (en) * 2008-07-30 2008-12-31 江苏工业学院 Quantitative applications process of natural mineral for dephosphorization for rich-phosphorus water body and phosphorus recovery
CN101337730A (en) * 2008-07-30 2009-01-07 江苏工业学院 Dephosphorization method for eutrophication water body or sewerage by natural mineral
CN101676223A (en) * 2008-09-19 2010-03-24 张宏 Quantitative application technology for removing and recovering phosphorus from water body with rich phosphorus or sewage using natural mineral
CN101734778A (en) * 2008-11-24 2010-06-16 江苏工业学院 Quantitative application process for removing phosphorous from phosphorous-enriched water by natural minerals
CN101823787A (en) * 2009-03-05 2010-09-08 江苏工业学院 Process for removing phosphorus from phosphorus water by using quantitative crystalline limestone and gypsum

Patent Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1333024A (en) * 2000-07-06 2002-01-30 佳木斯医学院制药厂 Injection for mammary sland recovery
CN101333024A (en) * 2008-07-30 2008-12-31 江苏工业学院 Quantitative applications process of natural mineral for dephosphorization for rich-phosphorus water body and phosphorus recovery
CN101337730A (en) * 2008-07-30 2009-01-07 江苏工业学院 Dephosphorization method for eutrophication water body or sewerage by natural mineral
CN101676223A (en) * 2008-09-19 2010-03-24 张宏 Quantitative application technology for removing and recovering phosphorus from water body with rich phosphorus or sewage using natural mineral
CN101734778A (en) * 2008-11-24 2010-06-16 江苏工业学院 Quantitative application process for removing phosphorous from phosphorous-enriched water by natural minerals
CN101823787A (en) * 2009-03-05 2010-09-08 江苏工业学院 Process for removing phosphorus from phosphorus water by using quantitative crystalline limestone and gypsum

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN110894095A (en) * 2018-05-15 2020-03-20 广西机电工业学校 Quantitative application process of natural minerals for removing phosphorus from phosphorus-rich water body
CN110498496A (en) * 2018-05-16 2019-11-26 广西机电工业学校 Technique for applying of the natural minerals to rich-phosphorus water body or sewage dephosphorization and recycling phosphorus

Similar Documents

Publication Publication Date Title
Hermassi et al. Phosphate recovery from aqueous solution by K-zeolite synthesized from fly ash for subsequent valorisation as slow release fertilizer
Wu Removal of Heavy Metal Ions from Industrial Wastewater Based on Chemical Precipitation Method.
Qiu et al. Enhanced nutrient removal in bioretention systems modified with water treatment residuals and internal water storage zone
CN102398936B (en) Composite preparation for inhibiting water blackening and smell and its preparation method and use method
CN101734778A (en) Quantitative application process for removing phosphorous from phosphorous-enriched water by natural minerals
CN101780421B (en) Ammonia nitrogen adsorbent and preparation method and application method thereof
Zhao et al. Dynamic changes of nitrogen and dissolved organic matter during the transport of mine water in a coal mine underground reservoir: Column experiments
Shi et al. Using modified quartz sand for phosphate pollution control in cemented phosphogypsum (PG) backfill
CN102241445A (en) Method for removing and recycling phosphorus from phosphorus-rich water bodies or sewage by using natural mineral mixture
CN102380343A (en) Simultaneous nitrogen and phosphorus removal modified artificial zeolite for micro-polluted water, and preparation method thereof
CN101676223A (en) Quantitative application technology for removing and recovering phosphorus from water body with rich phosphorus or sewage using natural mineral
Lin et al. Ammonium removal from digested effluent of swine wastewater by using solid residue from magnesium-hydroxide flue gas desulfurization process
Wu et al. Phosphorus recovery from waste activated sludge by sponge iron seeded crystallization of vivianite and process optimization with response surface methodology
Lv et al. Tertiary denitrification by sulfur/limestone packed biofilter
CN102276039A (en) Method for removing phosphorus from phosphorus-rich water body by natural mineral mixture
CN104973723A (en) Device and method for recycling phosphorus by virtue of induced crystallization
Zhao et al. Study on the feasibility and stability of drinking water treatment sludge (DWTS)@ zeolite to remove phosphorus from constructed wetlands
CN101333024A (en) Quantitative applications process of natural mineral for dephosphorization for rich-phosphorus water body and phosphorus recovery
CN100424014C (en) Method for extracting magnesium hydroxide from thick salt water using calcium carbide dreg
CN101823787A (en) Process for removing phosphorus from phosphorus water by using quantitative crystalline limestone and gypsum
Chen et al. Optimal regulation of N/P in horizontal sub-surface flow constructed wetland through quantitative phosphorus removal by steel slag fed
CN101337730A (en) Dephosphorization method for eutrophication water body or sewerage by natural mineral
CN202766378U (en) Two-stage advanced nitrogen and phosphorus synchronous removal device for sewage
Han et al. The characteristics and application of sludge-fly ash ceramic particles (SFCP) as novel filter media
CN103723854B (en) Method for intensive recovery of phosphorus in phosphorus-rich wastewater through applying polyacrylamide

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
C02 Deemed withdrawal of patent application after publication (patent law 2001)
WD01 Invention patent application deemed withdrawn after publication

Application publication date: 20111214