CN106295188A - The simple detection method of a kind of indoor particle float carcinogenic risk and device - Google Patents
The simple detection method of a kind of indoor particle float carcinogenic risk and device Download PDFInfo
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- CN106295188A CN106295188A CN201610658963.XA CN201610658963A CN106295188A CN 106295188 A CN106295188 A CN 106295188A CN 201610658963 A CN201610658963 A CN 201610658963A CN 106295188 A CN106295188 A CN 106295188A
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- 239000002245 particle Substances 0.000 title claims abstract description 83
- 230000000711 cancerogenic effect Effects 0.000 title claims abstract description 49
- 231100000315 carcinogenic Toxicity 0.000 title claims abstract description 49
- 238000001514 detection method Methods 0.000 title claims abstract description 18
- 231100000673 dose–response relationship Toxicity 0.000 claims abstract description 41
- 238000000034 method Methods 0.000 claims abstract description 16
- 231100000628 reference dose Toxicity 0.000 claims abstract description 15
- 239000000725 suspension Substances 0.000 claims description 10
- 206010028980 Neoplasm Diseases 0.000 claims description 9
- 201000011510 cancer Diseases 0.000 claims description 9
- 238000012502 risk assessment Methods 0.000 claims description 5
- 230000005183 environmental health Effects 0.000 abstract description 2
- 230000006870 function Effects 0.000 description 6
- 238000010168 coupling process Methods 0.000 description 3
- 238000005859 coupling reaction Methods 0.000 description 3
- 238000004519 manufacturing process Methods 0.000 description 3
- 230000008569 process Effects 0.000 description 3
- 230000008901 benefit Effects 0.000 description 2
- 238000004891 communication Methods 0.000 description 2
- 230000008878 coupling Effects 0.000 description 2
- 230000036541 health Effects 0.000 description 2
- 230000007774 longterm Effects 0.000 description 2
- 230000035800 maturation Effects 0.000 description 2
- 239000000203 mixture Substances 0.000 description 2
- 238000012545 processing Methods 0.000 description 2
- 239000000809 air pollutant Substances 0.000 description 1
- 231100001243 air pollutant Toxicity 0.000 description 1
- 210000004204 blood vessel Anatomy 0.000 description 1
- 238000004364 calculation method Methods 0.000 description 1
- 238000005516 engineering process Methods 0.000 description 1
- 238000011156 evaluation Methods 0.000 description 1
- 238000012854 evaluation process Methods 0.000 description 1
- 238000007689 inspection Methods 0.000 description 1
- 231100000915 pathological change Toxicity 0.000 description 1
- 230000036285 pathological change Effects 0.000 description 1
- 238000011160 research Methods 0.000 description 1
- 210000002345 respiratory system Anatomy 0.000 description 1
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- G—PHYSICS
- G01—MEASURING; TESTING
- G01N—INVESTIGATING OR ANALYSING MATERIALS BY DETERMINING THEIR CHEMICAL OR PHYSICAL PROPERTIES
- G01N15/00—Investigating characteristics of particles; Investigating permeability, pore-volume or surface-area of porous materials
- G01N15/06—Investigating concentration of particle suspensions
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- G—PHYSICS
- G16—INFORMATION AND COMMUNICATION TECHNOLOGY [ICT] SPECIALLY ADAPTED FOR SPECIFIC APPLICATION FIELDS
- G16H—HEALTHCARE INFORMATICS, i.e. INFORMATION AND COMMUNICATION TECHNOLOGY [ICT] SPECIALLY ADAPTED FOR THE HANDLING OR PROCESSING OF MEDICAL OR HEALTHCARE DATA
- G16H50/00—ICT specially adapted for medical diagnosis, medical simulation or medical data mining; ICT specially adapted for detecting, monitoring or modelling epidemics or pandemics
- G16H50/30—ICT specially adapted for medical diagnosis, medical simulation or medical data mining; ICT specially adapted for detecting, monitoring or modelling epidemics or pandemics for calculating health indices; for individual health risk assessment
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Abstract
The present invention is applicable to Environmental Health risk supervision technical field, it is provided that the simple detection method of a kind of indoor particle float carcinogenic risk and device.Described method includes: gather data, determines the average annual reconditioning of indoor particle float according to the described data gathered；Gather data, determine the Reference dose relation of suction chamber endoparticle float according to the described data gathered；According to reconditioning and dose response functional relationship, determine the carcinogenic risk of suction chamber endoparticle float.The present invention utilizes Reference dose relationship assessment to be exposed to the carcinogenic risk of indoor particle float for a long time.
Description
Technical field
The invention belongs to Environmental Health risk supervision technical field, particularly relate to a kind of indoor particle float carcinogenic risk
Simple detection method and device.
Background technology
Particle suspensions is one of common air pollutants, and the long-term particle suspensions that sucks can cause respiratory system, the heart
The pathological changes such as blood vessel, the indoor living space of people is the most unavoidably with the presence of a certain amount of particle suspensions.There are some researches show, greatly
In gas, the concentration of particle suspensions and mortality rate have positive correlation.
At present, the risk of developing cancer that may cause for long-term suction particle suspensions both at home and abroad has had the reality of maturation
Card data；Also the indoor particle float detector product of maturation is had on market.But also there is no measuring chamber endoparticle float
The method and apparatus of potential carcinogenic risk.
The simple detection of indoor particle float carcinogenic risk, it is possible to use the public understands the healthy wind of self local environment
Danger, in order to actively take prophylactico-therapeutic measures, thus reduce relevant health risk.
Summary of the invention
In consideration of it, the present invention provides simple detection method and the device of a kind of indoor particle float carcinogenic risk, permissible
The simple detection suction chamber endoparticle float impact on cancer incidence.
On the one hand, the present invention provides the simple detection method of a kind of indoor particle float carcinogenic risk, described method bag
Include:
Gathering data, described data include the day suction volume of indoor particle float；Described data according to gathering determine indoor
The average annual reconditioning of particle suspensions.
Gathering data, described data include the dose response parameter of suction chamber endoparticle float；According to gathering
Data determine the Reference dose relation of suction chamber endoparticle float.
According to reconditioning and dose response functional relationship, determine the carcinogenic risk of suction chamber endoparticle float.
On the other hand, the present invention provides the simple detection device of a kind of indoor particle float carcinogenic risk, described device
Including:
Reconditioning module, is used for gathering data, and described data include the day suction volume of indoor particle float, according to gather
Described data determine the average annual reconditioning of indoor particle float.
Dose response module, is used for gathering data, and described data include the dose response parameter of indoor particle float, root
The Reference dose relation of suction chamber endoparticle float is determined according to the described data gathered.
Carcinogenic risk module, according to reconditioning and dose response functional relationship, determines suction chamber endoparticle float
Carcinogenic risk.
The present invention compared with prior art exists and provides the benefit that: 1) directly gathers indoor particle float and exposes data
With dose response parameter, the accuracy of indoor particle float carcinogenic risk assessment can be improved；2) indoor particle of the present invention hangs
In the simple detection scheme of float carcinogenic risk, its algorithm can be by conventional statistic software and realizes, it is simple to improve inspection speed
Degree.The present invention carcinogenic risk by Reference dose Evaluation Room endoparticle float, prevents for production division and producers
Control health risk and foundation is provided, there is stronger usability and practicality.
Accompanying drawing explanation
For the technical scheme being illustrated more clearly that in the embodiment of the present invention, below will be to embodiment or description of the prior art
The accompanying drawing used required in is briefly described, it should be apparent that, the accompanying drawing in describing below is only some of the present invention
Embodiment, for those of ordinary skill in the art, on the premise of not paying creative work, it is also possible to according to these
Accompanying drawing obtains other accompanying drawing.
Fig. 1 is the flow process signal of the simple detection method of the indoor particle float carcinogenic risk that the embodiment of the present invention provides
Figure；
Fig. 2 is the composition structural representation of the simple detection device of the indoor particle float carcinogenic risk that the embodiment of the present invention provides
Figure.
Detailed description of the invention
In order to make the purpose of the present invention, technical scheme and advantage clearer, below in conjunction with drawings and Examples, right
The present invention is further elaborated.Should be appreciated that specific embodiment described herein only in order to explain the present invention, and
It is not used in the restriction present invention.
In order to technical solutions according to the invention are described, illustrate below by specific embodiment.
Embodiment of the method
The present embodiment provides the simple detection method of a kind of indoor particle float carcinogenic risk, sees Fig. 1, including step
S101, step S102 and step S103.
Step S101, gathers data, and described data include the day suction volume of indoor particle float.According to gathering
Data determine the average annual reconditioning of indoor particle float.
Concrete it may be that gather and include that the indoor particle float day of certain rubber manufacturing enterprise staff in 2016 sucks
Amount.
The described data reconditioning model that will gather, to determine the average annual reconditioning of indoor particle float, specifically
Formula is as follows:
P= ∑j c j ×/j (1)
Wherein: P is the average annual reconditioning of indoor particle float；For for the date；Cj is the suction of j day indoor particle float
Amount.
The above-mentioned data of 2016 are inputted indoor particle float reconditioning model, formula (1) institute can be calculated
The reconditioning related to, by can be calculated, the average annual reconditioning of indoor particle float is 37.09ug/m3。
Step S102, gathers data, and described data include the dose response parameter of suction chamber endoparticle float.According to adopting
The described data of collection determine the Reference dose relation of suction chamber endoparticle float.
Concrete it may be that gather and include certain rubber enterprise location cancer incidence in 2016；Indoor particle float
Average annual reconditioning.
The described data input dose-response model that will gather, to determine the dose response letter of suction chamber endoparticle float
Number relation, concrete formula is as follows:
D=R/I (2)
Wherein: D is dose response parameter, R is cancer incidence, and I is the average annual reconditioning of indoor particle float.
The above-mentioned data of 2016 are inputted the dose-response model of indoor particle float, formula (2) can be calculated
Involved Reference dose relation, by can be calculated, the Reference dose relation of indoor particle float is
0.173%, i.e. indoor particle float reconditioning often increases 1ug/m3, cancer incidence improves 0.173.
Step S103, according to reconditioning and dose response functional relationship, determines the carcinogenic of suction chamber endoparticle float
Risk.
Concrete it may be that by the average annual reconditioning obtained by step S101 and step S102 and dose response functional relationship
Input carcinogenic risk model, to determine the carcinogenic risk of suction chamber endoparticle float, concrete formula is as follows:
C=D × P (3)
Wherein: C is the carcinogenic risk of suction chamber endoparticle float, D is dose response parameter, and P is indoor particle float
Average annual reconditioning.
By data input carcinogenic risk model obtained by step S101 and step S102, the knot of formula (3) can be calculated
Really, by can be calculated, the carcinogenic risk of indoor particle float is 6.42, i.e. suction chamber endoparticle float makes cancer send out
Raw rate improves 6.42%.
So far, the carcinogenic risk evaluation process of indoor particle float is completed.
It should be noted that for aforesaid embodiment of the method, in order to be briefly described, therefore it is all expressed as a series of
Combination of actions, but those skilled in the art should know, and the present invention is not limited by described sequence of movement, because depending on
According to the present invention, some step can use other orders or carry out simultaneously.
Device embodiment:
The composition structural representation of the simple detection device of the indoor particle float carcinogenic risk that Fig. 2 provides for the embodiment of the present invention
Figure.For convenience of description, illustrate only the part relevant to the embodiment of the present invention.
The simple detection device of described indoor particle float carcinogenic risk can be to be built in terminal unit (such as individual
Computer, mobile phone, panel computer etc.) in the unit of software unit, hardware cell or software and hardware combining.
The simple detection device of described indoor particle float carcinogenic risk includes: reconditioning module 31, dose response
Module 32 and carcinogenic risk module 33, the concrete function of the most each module is as follows:
Reconditioning module 31, is used for gathering data, and described data include the day suction volume of indoor particle float, according to collection
Described data determine the average annual reconditioning of indoor particle float.
Dose response module 32, is used for gathering data, and described data include the dose response parameter of indoor particle float,
The Reference dose relation of suction chamber endoparticle float is determined according to the described data gathered.
Carcinogenic risk module 33, according to reconditioning and dose response functional relationship, determines suction chamber endoparticle float
Carcinogenic risk.
Further, described reconditioning module 31 includes:
Data acquisition unit 311, for gathering the day suction volume of indoor particle float.
Metering units 312, for the described data input reconditioning model that will gather, to determine indoor particle float
Average annual reconditioning, concrete formula is as follows:
P= ∑j c j ×/j
Wherein: P is the average annual reconditioning of indoor particle float；For for the date；CjSuction for j day indoor particle float
Amount.
Further, described dose response module 32 includes:
Data acquisition unit 321, for gathering the dose response parameter including indoor particle float.
Metering units 322, for the described data input dose-response model that will gather, to determine that suction chamber endoparticle hangs
The Reference dose relation of float, concrete formula is as follows:
D=R/I
Wherein: D is dose response parameter, R is cancer incidence, and I is the average annual reconditioning of indoor particle float.
Further, described carcinogenic risk module 33 includes:
Risk assessment unit 331, for inputting carcinogenic risk assessment models, with really by reconditioning and dose response functional relationship
Determining the carcinogenic risk of suction chamber endoparticle float, concrete formula is as follows:
C=D×P
Wherein: C is the carcinogenic risk of suction chamber endoparticle float, D is dose response parameter, and P is indoor particle float
Average annual reconditioning.
Those skilled in the art is it can be understood that arrive, for convenience of description and succinctly, only with above-mentioned each merit
Energy module, the division of unit are illustrated, and in actual application, can distribute above-mentioned functions by different as desired
Functional unit, module complete, and the internal structure of described device will be divided into different functional units or module, above to complete
The all or part of function described.Each functional module in embodiment, unit can be integrated in a processing unit, it is possible to
Being that unit is individually physically present, it is also possible to two or more unit are integrated in a unit, above-mentioned integrated
Unit both can realize to use the form of hardware, it would however also be possible to employ the form of SFU software functional unit realizes.It addition, each function mould
Block, unit specific name also only to facilitate mutually distinguish, be not limited to the protection domain of the application.Said apparatus
In each module, the specific works process of unit, be referred to the corresponding process in preceding method embodiment, do not repeat them here.
In several embodiments provided herein, it should be understood that disclosed apparatus and method, can be passed through it
Its mode realizes.Such as, device embodiment described above is only schematically, such as, and described module, the drawing of unit
Point, it is only a kind of logic function and divides, actual can have other dividing mode when realizing, and the most multiple unit or assembly can
To combine or to be desirably integrated into another system, or some features can be ignored, or does not performs.Another point, shown or beg for
The coupling each other of opinion or direct-coupling or communication connection can be the INDIRECT COUPLING by some interfaces, device or unit
Or communication connection, can be electrical, machinery or other form.
The described unit illustrated as separating component can be or may not be physically separate, shows as unit
The parts shown can be or may not be physical location, i.e. may be located at a place, or can also be distributed to multiple
On NE.Some or all of unit therein can be selected according to the actual needs to realize the mesh of the present embodiment scheme
's.
It addition, each functional module, unit in each embodiment of the present invention can be integrated in a processing unit, also
Can be that unit is individually physically present, it is also possible to two or more unit are integrated in a unit.Above-mentioned integrated
Unit both can realize to use the form of hardware, it would however also be possible to employ the form of SFU software functional unit realizes.
If described function is using the form realization of SFU software functional unit and as independent production marketing or use, permissible
It is stored in a computer read/write memory medium.Based on such understanding, technical scheme is the most in other words
The part contributing prior art or the part of this technical scheme can embody with the form of software product, this meter
Calculation machine software product is stored in a storage medium, including some instructions with so that a computer equipment (can be individual
People's computer, server, or the network equipment etc.) perform all or part of step of method described in each embodiment of the present invention.
And aforesaid storage medium includes: USB flash disk, portable hard drive, read only memory (ROM, Read-Only Memory), random access memory are deposited
The various media that can store program code such as reservoir (RAM, Random Access Memory), magnetic disc or CD.
Embodiment described above only in order to technical scheme to be described, is not intended to limit；Although with reference to aforementioned reality
Execute example the present invention has been described in detail, it will be understood by those within the art that: its still can to aforementioned respectively
Technical scheme described in embodiment is modified, or wherein portion of techniques feature is carried out equivalent；And these amendments
Or replace, do not make the essence of appropriate technical solution depart from spirit and the model of the embodiment of the present invention each embodiment technical scheme
Enclose.
Claims (8)
1. the simple detection method of an indoor particle float carcinogenic risk and device, it is characterised in that described method includes:
Gathering data, described data include the day suction volume of indoor particle float；Described data according to gathering determine indoor
The average annual reconditioning of particle suspensions；
Gathering data, described data include the dose response parameter of suction chamber endoparticle float；According to the described data gathered
Determine the Reference dose relation of suction chamber endoparticle float；
According to reconditioning and dose response functional relationship, determine the carcinogenic risk of suction chamber endoparticle float.
2. the method for claim 1, it is characterised in that described collection data, the described data according to gathering determine room
The average annual reconditioning of endoparticle float includes:
Gather the day suction volume of indoor particle float；The described data input reconditioning model that will gather, to determine indoor
The average annual reconditioning of particle suspensions, concrete formula is as follows:
P= ∑j c j ×/j (1)
Wherein: P is the average annual reconditioning of indoor particle float；For for the date；Cj is the suction of j day indoor particle float
Amount.
3. the method for claim 1, it is characterised in that described collection data, the described data according to gathering determine suction
The Reference dose relation entering indoor particle float includes:
Gather the dose response parameter of indoor particle float；The described data gathered are inputted the dosage of indoor particle float
Reaction model, to determine the Reference dose relation of suction chamber endoparticle float, concrete formula is as follows:
D=R/I (2)
Wherein: D is dose response parameter, R is cancer incidence, and I is the average annual reconditioning of indoor particle float.
4. the method for claim 1, it is characterised in that according to reconditioning and dose response functional relationship, determine suction
Entering the carcinogenic risk of indoor particle float, concrete formula is as follows:
C=D×P
Wherein: C is the carcinogenic risk of suction chamber endoparticle float, D is dose response parameter, and P is indoor particle float
Average annual reconditioning.
5. the simple detection device of an indoor particle float carcinogenic risk, it is characterised in that described device includes:
Reconditioning module, is used for gathering data, the day suction volume of described data room particle suspensions；According to gathering
Data determine the average annual reconditioning of indoor particle float；
Dose response module, is used for gathering data, the dose response parameter of described data room particle suspensions；According to gather
Described data determine the Reference dose relation of suction chamber endoparticle float；
Carcinogenic risk module, according to reconditioning and dose response functional relationship, determines the carcinogenic of suction chamber endoparticle float
Risk.
6. device as claimed in claim 5, it is characterised in that described reconditioning module includes:
Data acquisition unit, for gathering the day suction volume of indoor particle float；
Metering units, for the described data input reconditioning model that will gather, to determine the average annual of indoor particle float
Reconditioning；
Wherein, reconditioning model is as follows:
P= ∑j c j ×/j
Wherein: P is the average annual reconditioning of indoor particle float；For for the date；Cj is the suction of j day indoor particle float
Amount.
7. device as claimed in claim 5, it is characterised in that described dose response module includes:
Data acquisition unit, for gathering the dose response parameter of indoor particle float；
Metering units, the dose-response model of the described data input indoor particle float for gathering, to determine suction
The Reference dose relation of indoor particle float；
Wherein, dose-response model is as follows:
D=R/I
Wherein: D is dose response parameter, R is cancer incidence, and I is the average annual reconditioning of indoor particle float.
8. device as claimed in claim 5, it is characterised in that described carcinogenic risk module includes:
Risk assessment unit, for inputting carcinogenic risk assessment models, to determine by reconditioning and dose response functional relationship
The carcinogenic risk of suction chamber endoparticle float；
Wherein, the carcinogenic risk of indoor particle float is as follows:
C=D×P
Wherein: C is the carcinogenic risk of suction chamber endoparticle float, D is dose response parameter, and P is indoor particle float
Average annual reconditioning.
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