CN112374612B - Anti-blocking early warning system for constructed wetland - Google Patents

Anti-blocking early warning system for constructed wetland Download PDF

Info

Publication number
CN112374612B
CN112374612B CN202011226671.1A CN202011226671A CN112374612B CN 112374612 B CN112374612 B CN 112374612B CN 202011226671 A CN202011226671 A CN 202011226671A CN 112374612 B CN112374612 B CN 112374612B
Authority
CN
China
Prior art keywords
content
average
early warning
sewage
artificial wetland
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
Application number
CN202011226671.1A
Other languages
Chinese (zh)
Other versions
CN112374612A (en
Inventor
曹艺凡
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.)
Suzhou Yudeshui Electric Technology Co Ltd
Original Assignee
Suzhou Yudeshui Electric Technology Co 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 Suzhou Yudeshui Electric Technology Co Ltd filed Critical Suzhou Yudeshui Electric Technology Co Ltd
Priority to CN202011226671.1A priority Critical patent/CN112374612B/en
Publication of CN112374612A publication Critical patent/CN112374612A/en
Application granted granted Critical
Publication of CN112374612B publication Critical patent/CN112374612B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Images

Classifications

    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F3/00Biological treatment of water, waste water, or sewage
    • C02F3/32Biological treatment of water, waste water, or sewage characterised by the animals or plants used, e.g. algae
    • GPHYSICS
    • G01MEASURING; TESTING
    • G01KMEASURING TEMPERATURE; MEASURING QUANTITY OF HEAT; THERMALLY-SENSITIVE ELEMENTS NOT OTHERWISE PROVIDED FOR
    • G01K13/00Thermometers specially adapted for specific purposes
    • GPHYSICS
    • G01MEASURING; TESTING
    • G01NINVESTIGATING OR ANALYSING MATERIALS BY DETERMINING THEIR CHEMICAL OR PHYSICAL PROPERTIES
    • G01N33/00Investigating or analysing materials by specific methods not covered by groups G01N1/00 - G01N31/00
    • G01N33/18Water
    • GPHYSICS
    • G08SIGNALLING
    • G08BSIGNALLING OR CALLING SYSTEMS; ORDER TELEGRAPHS; ALARM SYSTEMS
    • G08B21/00Alarms responsive to a single specified undesired or abnormal condition and not otherwise provided for
    • G08B21/18Status alarms
    • G08B21/182Level alarms, e.g. alarms responsive to variables exceeding a threshold

Landscapes

  • Life Sciences & Earth Sciences (AREA)
  • Physics & Mathematics (AREA)
  • Chemical & Material Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • General Physics & Mathematics (AREA)
  • Health & Medical Sciences (AREA)
  • Pathology (AREA)
  • Biodiversity & Conservation Biology (AREA)
  • Biochemistry (AREA)
  • General Health & Medical Sciences (AREA)
  • Medicinal Chemistry (AREA)
  • Immunology (AREA)
  • Food Science & Technology (AREA)
  • Biotechnology (AREA)
  • Botany (AREA)
  • Analytical Chemistry (AREA)
  • Microbiology (AREA)
  • Hydrology & Water Resources (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Organic Chemistry (AREA)
  • Business, Economics & Management (AREA)
  • Emergency Management (AREA)
  • Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)

Abstract

The invention discloses an artificial wetland anti-clogging early warning system which comprises a sample sewage experiment module, a to-be-purified water source purification condition acquisition module and an early warning information output module, wherein the sample sewage experiment module is used for acquiring the purification treatment condition of the artificial wetland on sample sewage, the to-be-purified water source purification condition acquisition module is used for acquiring the initial purification treatment condition of the artificial wetland on the to-be-purified sewage and the purification treatment condition of the artificial wetland on the to-be-treated sewage after a plurality of detection periods, the early warning information output module outputs the early warning information of the artificial wetland according to the information acquired by the to-be-purified water source purification condition acquisition module, and the sample sewage experiment module comprises a sample data acquisition module before purification, a sample data acquisition module after purification and a first reference change rate calculation module.

Description

Constructed wetland prevents blockking up early warning system
Technical Field
The invention relates to the field of constructed wetlands, in particular to an anti-blocking early warning system for the constructed wetlands.
Background
The artificial wetland is a technology for treating sewage and sludge by using the physical, chemical and biological triple synergistic action of soil, artificial medium, plants and microorganisms in the process of flowing along a certain direction by using sewage and sludge which are controllably dosed to the artificially constructed wetland from the artificially constructed and controlled-operation ground similar to the marshland. After the operation time of the artificial wetland is too long, the wetland substrate is easy to block, the sewage treatment effect of the wetland is reduced, and even the operation life of the artificial wetland is possibly shortened.
Disclosure of Invention
The invention aims to provide an anti-blocking early warning system and method for an artificial wetland, which aim to solve the problems in the prior art.
In order to achieve the purpose, the invention provides the following technical scheme:
the utility model provides an constructed wetland prevents blockking up early warning system reaches, early warning system includes sample sewage experiment module, treats that the purification of water source condition obtains module and early warning information output module, sample sewage experiment module is used for obtaining the purification treatment condition of constructed wetland to sample sewage, treat that purification water source purification condition obtains the module and is used for obtaining the initial purification treatment condition of constructed wetland to the sewage of treating purifying and the purification treatment condition of constructed wetland to the sewage after a plurality of detection period, the early warning information output module is according to the early warning information of the information output constructed wetland that the purification water source condition of treating purifying obtained the module and acquireing.
Preferably, the sample sewage experiment module comprises a sample data acquisition module before purification, a sample data acquisition module after purification and a first reference change rate calculation module, wherein the sample data acquisition module before purification is used for acquiring the average content of nitrogen elements and the average content of phosphorus elements before the sample sewage is purified by the artificial wetland, the sample data acquisition module after purification is used for acquiring the average content of nitrogen elements and the average content of phosphorus elements after the sample sewage is purified by the artificial wetland, and the first reference change rate calculation module calculates a first reference change rate of nitrogen elements and a first reference change rate of phosphorus elements according to the average content of nitrogen elements and the average content of phosphorus elements before and after purification.
Preferably, the module for acquiring the purification condition of the water source to be purified comprises an initial purification data acquisition module, a suspended matter content judgment module, an oxygen content judgment module, a second reference change rate calculation module, a comprehensive reference change rate calculation module, a detection purification data acquisition module, a second blockage index calculation module and a third blockage index calculation module, wherein the initial purification data acquisition module acquires the average content of suspended matters, the average dissolved content of oxygen, the content of nitrogen and the content of phosphorus in the water source to be purified from the water inlet of the artificial wetland, and acquires the content of nitrogen and the content of phosphorus from the water outlet of the artificial wetland, the suspended matter content judgment module compares the average content of suspended matters acquired by the initial purification data acquisition module with the average content threshold of suspended matters, and reminds workers of preprocessing the water source to be purified when the average content of suspended matters is more than or equal to the average content threshold of suspended matters, the oxygen content judgment module compares the average dissolved oxygen content acquired by the initial purification data acquisition module with an average dissolved oxygen threshold value, and accordingly obtains a first blockage index, the second reference change rate calculation module calculates a second reference nitrogen change rate and a second reference phosphorus change rate according to the nitrogen content and the phosphorus content acquired by the initial purification data acquisition module at the artificial wetland inlet and outlet, the comprehensive reference change rate calculation module calculates a comprehensive reference nitrogen change rate and a comprehensive reference phosphorus change rate according to the first reference change rate and the second reference change rate, the detection purification data acquisition module comprises a nitrogen and phosphorus content acquisition module and a temperature acquisition module, and the nitrogen and phosphorus content acquisition module is used for acquiring the nitrogen content and the phosphorus content of the artificial wetland outlet after a plurality of detection periods, the temperature acquisition module is used for acquiring average temperature of each day in a plurality of detection periods, the second blockage index calculation module calculates a second blockage index according to the nitrogen element change rate, the phosphorus element change rate, the nitrogen element comprehensive reference change rate and the phosphorus element comprehensive reference change rate, and the third blockage index calculation module calculates a third blockage index according to the relation between the average temperature of each day and 10-20 ℃; the early warning information output module comprises an early warning index calculation module and an early warning index comparison module, the early warning index calculation module calculates an early warning index according to the first blockage index, the second blockage index and the third blockage index, and the early warning index comparison module compares the early warning index with an early warning index threshold value and outputs early warning information when the early warning index is larger than or equal to the early warning index threshold value.
An anti-blocking early warning method for an artificial wetland comprises the following steps:
step S1: obtaining the purification treatment condition of the constructed wetland on the sample sewage;
step S2: acquiring the initial purification treatment condition of the sewage to be purified of the artificial wetland;
step S3: and presetting a detection period T, and after n detection periods are separated, wherein the value of n is a natural number, acquiring the purification treatment condition of the artificial wetland to the treated sewage and outputting the early warning information of the artificial wetland.
Preferably, the step S1 further includes:
selecting a certain amount of sample sewage of M in advance, setting the average content Ny1 of nitrogen elements and the average content Py1 of phosphorus elements in the sample sewage, purifying the certain amount of sample sewage through the artificial wetland, collecting the purified sample sewage from a water outlet of the artificial wetland, collecting the average content Ny2 of the nitrogen elements and the average content Py2 of the phosphorus elements in the purified sample sewage when a certain amount of sample sewage of M is collected from the water outlet of the artificial wetland, and calculating a first reference change rate of the nitrogen elements, namely Cs1= (Ny1-Ny2)/Ny1 and a first reference change rate of the phosphorus elements, namely Ds1= (Py1-Py2)/Py 1.
Preferably, the step S2 further includes:
collecting the average content Xb of suspended matters in a water source to be purified from the water inlet of the artificial wetland, judging whether the average content Xb of the suspended matters is more than or equal to the threshold value of the average content of the suspended matters,
If the average content Xb of the suspended matters is more than or equal to the threshold value of the average content of the suspended matters, reminding a manager that the pretreatment for removing the suspended matters is carried out on the water source to be purified;
if the average content Xb of the suspended matters is smaller than the average content threshold of the suspended matters, acquiring the average dissolved oxygen content Ob, the nitrogen element content Nb and the phosphorus element content Pb of a water source to be purified at a water inlet, judging whether the average dissolved oxygen content Ob is smaller than or equal to the average dissolved oxygen content threshold Oy, if the average dissolved oxygen content Ob is smaller than or equal to the average dissolved oxygen content threshold Oy, judging that a first blockage index X = (Oy-Ob)/Oy, and if not, judging that the first blockage index X = 0;
collecting the content Na0 of nitrogen elements and the content Pa0 of phosphorus elements at the effluent of the artificial wetland, calculating a second reference change rate Cs2= (Nb-Na0)/Nb of the nitrogen elements, a second reference change rate Ds2= (Pb-Pa0)/Pb of the phosphorus elements,
then the overall reference rate of change of nitrogen Cz =0.4 Cs1+0.6 Cs2 and the overall reference rate of change of phosphorus Dz =0.4 Ds1+0.6 Ds 2.
Preferably, the step S3 further includes: step S31: after n detection periods, collecting the nitrogen element content Nan and the phosphorus element content Pan at the effluent of the artificial wetland,
after n detection periods are calculated, the nitrogen element change rate Csn '= (Nb-Nan)/Nb, the phosphorus element change rate Dsn' = (Pb-Pan)/Pb,
Then calculating a second occlusion index Y =0.5 (Cz-Csn ')/Cz +0.5 (Dz-Dsn')/Dz;
step S32: collecting the average temperature of the environment of the constructed wetland every day in the n detection periods,
if the average temperature in 40% of the days is 10 degrees or less, the day with the average temperature of 10 degrees or less is screened out, and the average temperature Td on the screened-out day is calculated, then the third clogging index Z = (10-Td)/10,
otherwise, if the average temperature in 60% of the days is greater than 20 degrees, screening out the days with the average temperature of greater than or equal to 20 degrees, and calculating the average temperature Tg of the screened-out days, then the third clogging index Z = (Tg-20)/20,
otherwise the third clogging index Z = 0;
step S33: and calculating an early warning index U = 0.3X + 0.5Y + 0.2Z, and reminding a manager that the constructed wetland needs to be nursed when the early warning index is greater than or equal to an early warning index threshold value so as to prevent the constructed wetland from further deteriorating and blocking.
Preferably, the duration of one detection period in step S3 is 14 days.
Compared with the prior art, the invention has the beneficial effects that: according to the invention, whether the constructed wetland has a blockage precursor is judged by collecting the oxygen content in the sewage to be purified, collecting the temperature of the environment where the constructed wetland is located and comparing the contents of nitrogen and phosphorus before and after the sewage to be purified is purified, so that the constructed wetland is repaired in time before the constructed wetland is blocked, and the service life of the constructed wetland is prolonged.
Drawings
FIG. 1 is a schematic block diagram of an anti-clogging early warning system for constructed wetlands according to the present invention;
fig. 2 is a schematic flow diagram of the anti-clogging early warning method for the constructed wetland.
Detailed Description
The technical solutions in the embodiments of the present invention will be clearly and completely described below with reference to the drawings in the embodiments of the present invention, and it is obvious that the described embodiments are only a part of the embodiments of the present invention, and not all of the embodiments. All other embodiments, which can be obtained by a person skilled in the art without making any creative effort based on the embodiments in the present invention, belong to the protection scope of the present invention.
Referring to fig. 1-2, in the embodiment of the invention, the early warning system comprises a sample sewage experiment module, a to-be-purified water source purification condition acquisition module and an early warning information output module, wherein the sample sewage experiment module is used for acquiring the purification treatment condition of the sample sewage by the artificial wetland, the to-be-purified water source purification condition acquisition module is used for acquiring the initial purification treatment condition of the sewage to be purified by the artificial wetland and the purification treatment condition of the sewage to be treated by the artificial wetland after a plurality of detection periods, and the early warning information output module outputs the early warning information of the artificial wetland according to the information acquired by the to-be-purified water source purification condition acquisition module.
The sample sewage experiment module comprises a sample data acquisition module before purification, a sample data acquisition module after purification and a first reference change rate calculation module, wherein the sample data acquisition module before purification is used for acquiring the average content of nitrogen elements and the average content of phosphorus elements before the sample sewage is purified by the artificial wetland, the sample data acquisition module after purification is used for acquiring the average content of nitrogen elements and the average content of phosphorus elements after the sample sewage is purified by the artificial wetland, and the first reference change rate calculation module calculates a first reference change rate of nitrogen elements and a first reference change rate of phosphorus elements according to the average content of nitrogen elements and the average content of phosphorus elements before and after purification.
The module for acquiring the purification condition of the water source to be purified comprises an initial purification data acquisition module, a suspended matter content judgment module, an oxygen content judgment module, a second reference change rate calculation module, a comprehensive reference change rate calculation module, a detection purification data acquisition module, a second blockage index calculation module and a third blockage index calculation module, wherein the initial purification data acquisition module acquires the average content of suspended matters, the average dissolved content of oxygen, the content of nitrogen and the content of phosphorus in the water source to be purified from the water inlet of the artificial wetland, and the acquired content of nitrogen and the acquired content of phosphorus from the water outlet of the artificial wetland, the suspended matter content judgment module compares the average content of suspended matters acquired by the initial purification data acquisition module with the average content threshold of suspended matters, and reminds workers to preprocess the water source to be purified when the average content of suspended matters is more than or equal to the average content threshold of suspended matters, the oxygen content judgment module compares the average dissolved oxygen content acquired by the initial purification data acquisition module with an average dissolved oxygen threshold value, and accordingly obtains a first blockage index, the second reference change rate calculation module calculates a second reference nitrogen change rate and a second reference phosphorus change rate according to the nitrogen content and the phosphorus content acquired by the initial purification data acquisition module at the artificial wetland inlet and outlet, the comprehensive reference change rate calculation module calculates a comprehensive reference nitrogen change rate and a comprehensive reference phosphorus change rate according to the first reference change rate and the second reference change rate, the detection purification data acquisition module comprises a nitrogen and phosphorus content acquisition module and a temperature acquisition module, and the nitrogen and phosphorus content acquisition module is used for acquiring the nitrogen content and the phosphorus content of the artificial wetland outlet after a plurality of detection periods, the temperature acquisition module is used for acquiring average temperature of each day in a plurality of detection periods, the second blockage index calculation module calculates a second blockage index according to the nitrogen element change rate, the phosphorus element change rate, the nitrogen element comprehensive reference change rate and the phosphorus element comprehensive reference change rate, and the third blockage index calculation module calculates a third blockage index according to the relation between the average temperature of each day and 10-20 ℃; the early warning information output module comprises an early warning index calculation module and an early warning index comparison module, the early warning index calculation module calculates an early warning index according to the first blockage index, the second blockage index and the third blockage index, and the early warning index comparison module compares the early warning index with an early warning index threshold value and outputs early warning information when the early warning index is larger than or equal to the early warning index threshold value.
An anti-blocking early warning method for an artificial wetland comprises the following steps:
step S1: obtaining the purification treatment condition of the constructed wetland on the sample sewage:
selecting a certain amount of sample sewage of M in advance, setting the average content Ny1 of nitrogen elements and the average content Py1 of phosphorus elements in the sample sewage, purifying the certain amount of sample sewage through the artificial wetland, collecting the purified sample sewage from a water outlet of the artificial wetland, collecting the average content Ny2 of the nitrogen elements and the average content Py2 of the phosphorus elements in the purified sample sewage when a certain amount of sample sewage of M is collected from the water outlet of the artificial wetland, and calculating a first reference change rate of the nitrogen elements, namely Cs1= (Ny1-Ny2)/Ny1 and a first reference change rate of the phosphorus elements, namely Ds1= (Py1-Py2)/Py 1; when a certain amount M of sample sewage is selected, the suspended matter content of the sample sewage is lower than the suspended matter average content threshold value, and the oxygen dissolved content is higher than the oxygen average dissolved amount threshold value, so that an ideal state of the constructed wetland for sewage purification is obtained;
step S2: acquiring the initial purification treatment condition of the sewage to be purified of the artificial wetland:
collecting the average content Xb of suspended matters in a water source to be purified from the water inlet of the artificial wetland, judging whether the average content Xb of the suspended matters is more than or equal to the threshold value of the average content of the suspended matters,
If the average content Xb of the suspended matters is more than or equal to the threshold value of the average content of the suspended matters, reminding a manager that the pretreatment for removing the suspended matters is carried out on the water source to be purified;
if the average content Xb of the suspended matters is smaller than the average content threshold of the suspended matters, acquiring the average dissolved oxygen content Ob, the nitrogen element content Nb and the phosphorus element content Pb of a water source to be purified at a water inlet, judging whether the average dissolved oxygen content Ob is smaller than or equal to the average dissolved oxygen content threshold Oy, if the average dissolved oxygen content Ob is smaller than or equal to the average dissolved oxygen content threshold Oy, judging that a first blockage index X = (Oy-Ob)/Oy, and if not, judging that the first blockage index X = 0;
collecting the content Na0 of nitrogen elements and the content Pa0 of phosphorus elements at the effluent of the artificial wetland, calculating a second reference change rate Cs2= (Nb-Na0)/Nb of the nitrogen elements, a second reference change rate Ds2= (Pb-Pa0)/Pb of the phosphorus elements,
then the overall reference rate of change of nitrogen Cz =0.4 Cs1+0.6 Cs2 and the overall reference rate of change of phosphorus Dz =0.4 Ds1+0.6 Ds 2.
Step S3: presetting a detection period T, and after detecting at intervals of n detection periods, acquiring the purification treatment condition of the artificial wetland to-be-treated sewage at the moment and outputting early warning information of the artificial wetland:
step S31: after n detection periods, collecting the nitrogen element content Nan and the phosphorus element content Pan at the effluent of the constructed wetland, wherein the value of n is a natural number,
After n detection periods are calculated, the nitrogen element change rate Csn '= (Nb-Nan)/Nb, the phosphorus element change rate Dsn' = (Pb-Pan)/Pb,
then calculating a second occlusion index Y =0.5 (Cz-Csn ')/Cz +0.5 (Dz-Dsn')/Dz;
for example, when 1 detection cycle is separated, the nitrogen content of the effluent of the artificial wetland is Na1 and the phosphorus content of the effluent of the artificial wetland is Pa1, the nitrogen change rate Cs1= (Nb-Na1)/Nb, the phosphorus change rate Ds1= (Pb-Pa1)/Pb, and the second blockage index Y =0.5 = (Cz-Cs1)/Cz +0.5 = (Dz-Ds1)/Dz, during the actual operation process, the condition of purified sewage of the artificial wetland can be detected after each detection cycle, an early warning index is obtained, and whether the artificial wetland is nursed or not is judged;
step S32: collecting the average temperature of the environment of the constructed wetland every day in the n detection periods,
if the average temperature in 40% days is less than or equal to 10 ℃, screening out days with the average temperature less than or equal to 10 ℃, and calculating the average temperature Td of the screened days, wherein the third clogging index Z = (10-Td)/10, when the temperature is lower, the activity of microorganisms in the constructed wetland is lower, and the microorganisms cannot be effectively degraded in time, so that the constructed wetland is easy to clog;
Otherwise, if the average temperature in 60% of days is higher than 20 ℃, screening out days with the average temperature being higher than or equal to 20 ℃, and calculating the average temperature Tg of the screened days, wherein the third blockage index Z = (Tg-20)/20, and when the temperature is higher, the growth and reproduction speed of microorganisms and plants in the artificial wetland is too high, so that the artificial wetland is easy to block;
otherwise the third clogging index Z = 0;
step S33: and calculating an early warning index U = 0.3X + 0.5Y + 0.2Z, and reminding a manager that the constructed wetland needs to be nursed when the early warning index is greater than or equal to an early warning index threshold value so as to prevent the constructed wetland from further deteriorating and blocking.
It will be evident to those skilled in the art that the invention is not limited to the details of the foregoing illustrative embodiments, and that the present invention may be embodied in other specific forms without departing from the spirit or essential attributes thereof. The present embodiments are therefore to be considered in all respects as illustrative and not restrictive, the scope of the invention being indicated by the appended claims rather than by the foregoing description, and all changes which come within the meaning and range of equivalency of the claims are therefore intended to be embraced therein.

Claims (1)

1. The utility model provides an constructed wetland prevents blockking up early warning system which characterized in that: the early warning system comprises a sample sewage experiment module, a to-be-purified water source purification condition acquisition module and an early warning information output module, wherein the sample sewage experiment module is used for acquiring the purification treatment condition of the constructed wetland on sample sewage, the to-be-purified water source purification condition acquisition module is used for acquiring the initial purification treatment condition of the constructed wetland on the to-be-purified sewage and the purification treatment condition of the constructed wetland on the to-be-treated sewage after a plurality of detection periods, and the early warning information output module outputs early warning information of the constructed wetland according to the information acquired by the to-be-purified water source purification condition acquisition module;
the anti-blocking early warning method of the anti-blocking early warning system for the constructed wetland comprises the following steps:
step S1: obtaining the purification treatment condition of the constructed wetland on the sample sewage;
step S2: acquiring the initial purification treatment condition of the sewage to be purified of the artificial wetland;
step S3: presetting a detection period T, and after n detection periods are spaced, acquiring the purification treatment condition of the artificial wetland to-be-treated sewage at the moment and outputting early warning information of the artificial wetland;
the step S1 further includes:
Selecting a certain amount of sample sewage of M in advance, setting the average content Ny1 of nitrogen elements and the average content Py1 of phosphorus elements in the sample sewage, purifying the certain amount of sample sewage through the artificial wetland, collecting the purified sample sewage from a water outlet of the artificial wetland, collecting the average content Ny2 of the nitrogen elements and the average content Py2 of the phosphorus elements in the purified sample sewage when a certain amount of sample sewage of M is collected from the water outlet of the artificial wetland, and calculating a first reference change rate of the nitrogen elements, namely Cs1= (Ny1-Ny2)/Ny1 and a first reference change rate of the phosphorus elements, namely Ds1= (Py1-Py2)/Py 1;
the step S2 further includes:
collecting the average content Xb of suspended matters in a water source to be purified from the water inlet of the artificial wetland, judging whether the average content Xb of the suspended matters is more than or equal to the threshold value of the average content of the suspended matters,
if the average content Xb of the suspended matters is more than or equal to the threshold value of the average content of the suspended matters, reminding a manager that the pretreatment for removing the suspended matters is carried out on the water source to be purified firstly;
if the average content Xb of the suspended matters is smaller than the average content threshold of the suspended matters, acquiring the average dissolved oxygen content Ob, the nitrogen element content Nb and the phosphorus element content Pb of a water source to be purified at a water inlet, judging whether the average dissolved oxygen content Ob is smaller than or equal to the average dissolved oxygen content threshold Oy, if the average dissolved oxygen content Ob is smaller than or equal to the average dissolved oxygen content threshold Oy, judging that a first blockage index X = (Oy-Ob)/Oy, and if not, judging that the first blockage index X = 0;
Collecting the content Na0 of nitrogen elements and the content Pa0 of phosphorus elements at the effluent of the artificial wetland, calculating a second reference change rate Cs2= (Nb-Na0)/Nb of the nitrogen elements, a second reference change rate Ds2= (Pb-Pa0)/Pb of the phosphorus elements,
then the overall reference rate of change of nitrogen Cz =0.4 Cs1+0.6 Cs2, the overall reference rate of change of phosphorus Dz =0.4 Ds1+0.6 Ds 2;
the step S3 further includes:
step S31: after n detection periods, collecting the nitrogen element content Nan and the phosphorus element content Pan at the effluent of the constructed wetland, wherein the value of n is a natural number,
after n detection periods are calculated, the nitrogen element change rate Csn '= (Nb-Nan)/Nb, the phosphorus element change rate Dsn' = (Pb-Pan)/Pb,
then calculating a second occlusion index Y =0.5 (Cz-Csn ')/Cz +0.5 (Dz-Dsn')/Dz;
step S32: collecting the average temperature of the environment of the constructed wetland every day in the n detection periods,
if the average temperature in 40% of the days is 10 degrees or less, the day with the average temperature of 10 degrees or less is screened out, and the average temperature Td on the screened-out day is calculated, then the third clogging index Z = (10-Td)/10,
otherwise, if the average temperature in 60% of the days is greater than 20 degrees, screening out the days with the average temperature of greater than or equal to 20 degrees, and calculating the average temperature Tg of the screened-out days, then the third clogging index Z = (Tg-20)/20,
Otherwise the third clogging index Z = 0;
step S33: calculating an early warning index U = 0.3X + 0.5Y + 0.2Z, and reminding a manager that the artificial wetland needs to be nursed when the early warning index is greater than or equal to an early warning index threshold value so as to prevent the artificial wetland from further deteriorating and blocking;
the duration of one detection period in step S3 is 14 days.
CN202011226671.1A 2020-04-02 2020-04-02 Anti-blocking early warning system for constructed wetland Active CN112374612B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN202011226671.1A CN112374612B (en) 2020-04-02 2020-04-02 Anti-blocking early warning system for constructed wetland

Applications Claiming Priority (2)

Application Number Priority Date Filing Date Title
CN202011226671.1A CN112374612B (en) 2020-04-02 2020-04-02 Anti-blocking early warning system for constructed wetland
CN202010254941.3A CN111392868B (en) 2020-04-02 2020-04-02 Anti-blocking early warning system and method for constructed wetland

Related Parent Applications (1)

Application Number Title Priority Date Filing Date
CN202010254941.3A Division CN111392868B (en) 2020-04-02 2020-04-02 Anti-blocking early warning system and method for constructed wetland

Publications (2)

Publication Number Publication Date
CN112374612A CN112374612A (en) 2021-02-19
CN112374612B true CN112374612B (en) 2022-07-29

Family

ID=71425966

Family Applications (2)

Application Number Title Priority Date Filing Date
CN202010254941.3A Active CN111392868B (en) 2020-04-02 2020-04-02 Anti-blocking early warning system and method for constructed wetland
CN202011226671.1A Active CN112374612B (en) 2020-04-02 2020-04-02 Anti-blocking early warning system for constructed wetland

Family Applications Before (1)

Application Number Title Priority Date Filing Date
CN202010254941.3A Active CN111392868B (en) 2020-04-02 2020-04-02 Anti-blocking early warning system and method for constructed wetland

Country Status (1)

Country Link
CN (2) CN111392868B (en)

Families Citing this family (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN112861323B (en) * 2021-01-15 2022-09-30 河海大学 Method for calculating biological blockage of constructed wetland
CN115712286B (en) * 2022-11-29 2023-05-12 淮北师范大学 Sewage treatment supervision system for constructed wetland
CN118359299B (en) * 2024-06-18 2024-08-27 安徽新宇环保科技股份有限公司 Rural domestic sewage treatment device and method

Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN105045945A (en) * 2015-04-20 2015-11-11 中国水产科学研究院黄海水产研究所 Method for quickly constructing economical and efficient artificial wetland
CN106396264A (en) * 2016-10-13 2017-02-15 华中科技大学 Artificial wetland sewage treatment system capable of preventing blockage
CN206680262U (en) * 2017-01-20 2017-11-28 北京正和恒基城市规划设计研究院有限公司 Anti-clogging artificial wet land system

Family Cites Families (12)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS56144796A (en) * 1980-04-10 1981-11-11 Toshiba Corp Disposer for water in ditch discharged from plant
JPS62250998A (en) * 1986-04-23 1987-10-31 Agency Of Ind Science & Technol Hydroponic type purifying fence
JPWO2005068379A1 (en) * 2004-01-13 2007-08-23 伊藤忠林業株式会社 Wastewater purification system
JP5358886B2 (en) * 2007-02-22 2013-12-04 栗田工業株式会社 Biological treatment method of water containing organic matter
US7927484B2 (en) * 2008-09-11 2011-04-19 University Of Central Florida Research Foundation, Inc. Passive underground drainfield for septic tank nutrient removal using functionalized green filtration media
CN102249420A (en) * 2011-06-03 2011-11-23 中国海洋大学 Vertical undercurrent constructed wetland for treating polluted river water
CN105152317B (en) * 2015-08-28 2017-08-01 北京金控数据技术股份有限公司 The method that early warning is carried out to the film properties of membrane bioreactor
CN105217795B (en) * 2015-10-30 2016-04-20 北京金泽环境能源技术研究有限公司 A kind of method and system of on-line automatic block clearing artificial swamp
CN106242070B (en) * 2016-10-26 2019-03-26 青岛大学 A kind of automated sewage processing system and its control method based on artificial swamp
KR101797527B1 (en) * 2016-12-16 2017-11-14 코오롱환경서비스주식회사 A waste water treatment apparatus with a function of preventing biocube screen blocking
CN109607632A (en) * 2018-12-25 2019-04-12 湖南智水环境设备有限公司 The control system of sewage disposal device
CN110921833B (en) * 2019-12-26 2021-09-24 暨南大学 Sewage treatment system and method for strengthening anaerobic ammonia oxidation denitrification and phosphorus removal of domestic sewage

Patent Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN105045945A (en) * 2015-04-20 2015-11-11 中国水产科学研究院黄海水产研究所 Method for quickly constructing economical and efficient artificial wetland
CN106396264A (en) * 2016-10-13 2017-02-15 华中科技大学 Artificial wetland sewage treatment system capable of preventing blockage
CN206680262U (en) * 2017-01-20 2017-11-28 北京正和恒基城市规划设计研究院有限公司 Anti-clogging artificial wet land system

Also Published As

Publication number Publication date
CN111392868A (en) 2020-07-10
CN111392868B (en) 2020-12-22
CN112374612A (en) 2021-02-19

Similar Documents

Publication Publication Date Title
CN112374612B (en) Anti-blocking early warning system for constructed wetland
CN103864194A (en) Emergency control method for sewage treatment system for treating abnormal influent/effluent quality
CN111470628B (en) Carbon source medicament adding equipment and adding method
Fanta et al. Phosphorus removal from industrial discharge impacted municipal wastewater using sequencing batch moving bed biofilm reactor
CN118047476B (en) River and lake water quality intelligent monitoring regulation and control system
CN115423384A (en) Distributed sewage collection and cyclic utilization system and method based on artificial intelligence
CN108217983B (en) Pulse type water quality purifying system and river sewage treatment method
CN115028269A (en) Regional water pollution treatment method
CN118095664A (en) Sponge type viaduct ecological water collecting system and method
CN117361769A (en) Rural sewage treatment system and method
CN111807615A (en) Nitrogen and phosphorus interception and purification system for farmland surface runoff
CN103319050B (en) Ecological safety purifying method for sewage of rivers and channels
CN108399494A (en) Combined system regional pollution load abatement interception ratio determines method
CN116011857A (en) Cascade hydropower station interval flow calculation method and device
CN212609810U (en) Multi-condition controlled automatic back-flushing device for denitrification biological filter
CN112960865A (en) Ecological management method for coal mining subsidence area
CN201864645U (en) Sewage treatment recycling device capable of being monitored
CN209974545U (en) Farmland irrigation drainage purification treatment circulation system
CN212356697U (en) Agricultural non-point source pollution treatment system for river channel purification
Robles-Rodriguez et al. A simple model of wastewater treatment plants for managing the quality of the Seine River
CN208327725U (en) A kind of equally distributed artificial swamp of sewage
Taesopapong et al. Innovative eco biofilter/membrane bioreactor (MBR) technology for community wastewater recycling
CN111732283A (en) Sewage purification treatment system
JP4309645B2 (en) Flocculant injection control method and apparatus
CN203999249U (en) A kind of blodisc with inclined ribs disc

Legal Events

Date Code Title Description
PB01 Publication
PB01 Publication
SE01 Entry into force of request for substantive examination
SE01 Entry into force of request for substantive examination
TA01 Transfer of patent application right
TA01 Transfer of patent application right

Effective date of registration: 20220712

Address after: 215010 room 704, building 5, No. 556, Changjiang Road, high tech Zone, Suzhou, Jiangsu

Applicant after: SUZHOU YUDESHUI ELECTRICAL TECHNOLOGY Co.,Ltd.

Address before: No.96 Tianpu Road, Pukou District, Nanjing, Jiangsu 210000

Applicant before: Cao Yifan

GR01 Patent grant
GR01 Patent grant