CN110941930A - Method for simulating PM2.5 diffusion condition of Mongolian Uulan Batot city - Google Patents

Method for simulating PM2.5 diffusion condition of Mongolian Uulan Batot city Download PDF

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CN110941930A
CN110941930A CN201911050496.2A CN201911050496A CN110941930A CN 110941930 A CN110941930 A CN 110941930A CN 201911050496 A CN201911050496 A CN 201911050496A CN 110941930 A CN110941930 A CN 110941930A
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mongolian
city
diffusion
unhealthy
uulan
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高纳
赵林
孙袭明
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Tianjin University
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    • G01MEASURING; TESTING
    • G01NINVESTIGATING OR ANALYSING MATERIALS BY DETERMINING THEIR CHEMICAL OR PHYSICAL PROPERTIES
    • G01N15/00Investigating characteristics of particles; Investigating permeability, pore-volume, or surface-area of porous materials
    • G01N15/06Investigating concentration of particle suspensions
    • G01N15/075

Abstract

The invention relates to a PM2.5 diffusion simulation diagram of Mongolian Uvaria city, which is characterized in that 2018 year-one-year data of 8 CAM monitoring stations are processed by an inverse distance weighting method (IDW), the PM2.5 diffusion simulation diagram of the Mongolian Uvaria city is drawn by taking months and seasons as units, and the PM2.5 level is classified according to human health related Air Quality Index (AQI) of Environmental Protection Agency (EPA). The method has the advantages that the PM2.5 pollution diffusion condition of an unmeasured area is accurately simulated and predicted, the chimney in the Mongolian yurt area is proved to be a main PM2.5 pollutant source, researchers and clients can clearly and definitely know the fine particulate matter diffusion condition of Mongolian Uulan Butot, and the method is also a basic information basis for carrying out related measures for reducing the fine particulate matter.

Description

Method for simulating PM2.5 diffusion condition of Mongolian Uulan Batot city
Technical Field
The invention belongs to environmental science and air pollution research, accurately simulates and predicts the PM2.5 pollution diffusion condition of an unmeasured area, proves that a chimney in a Mongolian yurt area is a main PM2.5 pollutant source, and can enable researchers and clients to clearly and clearly know the fine particulate matter diffusion condition of Mongolian Uulan baset. In addition, it is the basic information basis for the implementation of relevant measures for reducing fine particulate matter.
Background
At present, air pollution in Wulanbai city is the first problem to be solved urgently. Wherein the fine particulate pollution accounts for 80% of the total air pollution, and is mainly from fire coal in Mongolian yurt areas. Has exceeded the world health organization air quality guidelines and the Mongolian fine particulate pollution standards. Moreover, it is becoming a major factor in respiratory diseases. Therefore, it is necessary to measure and simulate the diffusion of PM2.5 in the city of wulanduto. Based on the PM2.5 diffusion simulation diagram, the main particulate matter generation source and the healthy exposure condition can be determined, and the basis for implementing air pollution treatment measures is provided.
In Wulandutong, the locations of Continuous Air Monitoring (CAM) sites are sparse and there is a lack of facility and satellite data for high resolution measurement of the spread of atmospheric pollution areas in Wulanduton. Therefore, there is a need for relevant simulation and prediction of air pollution in unmeasured areas.
Disclosure of Invention
The invention aims to overcome the defects of the prior art and provide a novel simulation method for PM2.5 diffusion conditions of Mongolian Ukrabbe to overcome the defect of PM2.5 diffusion information data of Mongolian Ukrabbe.
The method applies an Inverse Distance Weighting (IDW) method to predict atmospheric pollution conditions. IDW is a deterministic method of spatial interpolation. Unknown position "zpThe value at "is calculated as a weighted average of the monitoring station measurements. The method assumes "zpThe value is affected more by the close-range measurement than by the far-range measurement. In other words, closer positions get higher weights, which decrease with distance. The contaminant measurement at "n" around the unknown position is known as i 1.… … n, value "z" at unknown positionp"calculate as:
Figure BDA0002255214120000011
Zppredicted value
Z1Measured value
d1 pTo the p power of the distance
n i=1Sum of nearest points
To plot PM2.5 pollution, annual data from 2018 months 1 to 12 months 31 days of 8 CAM monitoring stations were measured using an ENVEA automated nephelometer. The 8 monitoring stations belong to the Meteorological and environmental monitoring Bureau of Wulanbarton and two government agencies for reducing air pollution. In these sites, NO is measured once per hourx,SO2CO, PM10, PM2.5 and O3A contaminant. The invention selects the measurement data of PM2.5 and processes the data by taking months and seasons as units.
Drawings
FIG. 1 is a PM2.5 distribution plot (. mu.g/m)3);
FIG. 2 is a graph of year-round measurement data for various continuous air monitoring stations.
Detailed Description
The invention is further described with reference to the following figures and specific examples.
Diurnal PM2.5 data is processed in units of months and seasons, and PM2.5 levels are classified into the following categories according to the Environmental Protection Agency (EPA) human health related Air Quality Index (AQI): 0-12 mu g/m3Is good, 12.1-35.4 mu g/m3Is 'middle' 35.5-55.4 mu g/m3Is unhealthy for sensitive people, and has a concentration of 55.5-150.4 μ g/m3Is unhealthy, 150.5-250.4 μ g/m3Is "very unhealthy" and is greater than 250.5 μ g/m3Is "dangerous".
In fig. 1, the winter Mongolian climate is very cold (one of the coldest headquarters in the world), so homes in Mongolian regions use coal fuel (and a small amount of wood) for heating and cooking. PM2.5 emissions sometimes reach 900. mu.g/m3Particularly in the areas "Bayankhoshuu", "Zunsalaa" and "Tolgoit", in black and brown. The average PM2.5 value in winter is about 250 mu g/m3
In spring, the Wulan Barton climate is windy and warm, and the average emission of PM2.5 is reduced to 55 mu g/m3. In early spring (3 months), the weather is cold, and the families in the Mongolian yurt area still use coal fuel.
The summer season of Ulandubator is hot and dryAnd (4) seasons. PM2.5 emissions are relatively low. But still a small amount of PM2.5 emissions of about 35. mu.g/m3. The PM2.5 is emitted as fugitive dust from unpaved roads and construction activities. As 90% of the yurt areas still have unpaved roads. Therefore, PM2.5 is distributed evenly throughout the urban area and is referred to as "medium yellow". Some areas are fresh and air, indicated by "white" on the map.
The autumn climate of Wulanbaoto is cooler and warmer than the winter. Therefore, PM2.5 is distributed evenly throughout the urban area. At this time, the average concentrations of PM2.5 at the beginning and end of the season were 40. mu.g/m3And 100. mu.g/m3
8 monitoring stations were selected, each located at a position as shown in Table 1. The monitoring stations respectively monitor the PM2.5 conditions of the Mongolian yurt area, the apartment area and the industrial area.
Table 1 CAM monitoring station selected
Figure BDA0002255214120000031
In fig. 2, the PM2.5 measurements for each day for 8 monitoring stations are graphically represented. As can be seen from the figure, it is consistent with the national standard (50. mu.g/m)3Indicated by "red line") the PM2.5 emissions monitored at each station exceed national standards, in particular 10 months to 4 months (cold season of the year), and sometimes even more than 800 μ g/m3Or 16 times over the national standard.

Claims (3)

1. A method for simulating PM2.5 diffusion of Mongolian Uulanbarton city is characterized by comprising the following steps:
(1) using Inverse Distance Weighting (IDW), establishing "z" at the unknown locationp"calculation formula of value;
(2) measuring data of a certain whole year of 8 CAM monitoring sites by using an ENVEA automatic turbidity meter;
(3) drawing a PM2.5 diffusion simulation diagram of Mongolian Ukraubato city by taking months and seasons as units according to the collected data;
(4) the PM2.5 levels were classified according to the Environmental Protection Agency (EPA) human health related Air Quality Index (AQI).
2. The method of claim 1, wherein the Inverse Distance Weighting (IDW) method is based on the assumption of "zpThe value is affected more by the close-range measurement than by the far-range measurement.
3. The method of claim 1, wherein the PM2.5 levels are classified according to human health-related Air Quality Index (AQI), wherein the PM2.5 levels are 0-12 μ g/m3Is good, 12.1-35.4 mu g/m3Is 'middle' 35.5-55.4 mu g/m3Is unhealthy for sensitive people, and has a concentration of 55.5-150.4 μ g/m3Is unhealthy, 150.5-250.4 μ g/m3Is "very unhealthy" and is greater than 250.5 μ g/m3Is "dangerous".
CN201911050496.2A 2019-10-31 2019-10-31 Method for simulating PM2.5 diffusion condition of Mongolian Uulan Batot city Pending CN110941930A (en)

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Citations (5)

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CN106446401A (en) * 2016-09-22 2017-02-22 天津大学 PM2.5 visualized dynamic diffusion simulation system based on GIS
CN106844626A (en) * 2017-01-20 2017-06-13 武汉大学 Using microblogging keyword and the method and system of positional information simulated air quality
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US20160091474A1 (en) * 2014-09-29 2016-03-31 Tanguy Griffon Method and a System for Determining at Least One Forecasted Air Quality Health Effect Caused in a Determined Geographical Area by at Least One Air Pollutant
CN104834821A (en) * 2015-05-13 2015-08-12 中国环境科学研究院 Method for determining population exposure area according to environmental health risk assessment on river pollution specific pollutants and application of method
CN106446401A (en) * 2016-09-22 2017-02-22 天津大学 PM2.5 visualized dynamic diffusion simulation system based on GIS
CN106844626A (en) * 2017-01-20 2017-06-13 武汉大学 Using microblogging keyword and the method and system of positional information simulated air quality
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