Presentation Pavlovic Vojvodina

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    UNIVERSITYPOLITEHNICAof TIMISOARAEUROPEAN UNION

    GOVERNMENT OF ROMANIA GOVERNMENT OF THE REPUBLICOF SERBIA

    Structural Funds2007 - 2013

    Project title: Sustainable development for Banat Region by means of education andscientific research & development in transboundary air quality monitoring issues

    Prof.Dr.ingMilan Pavlovic

    Results of the Air Quality Monitoring Campaign

    Zrenjan in, 05.08. 10.08.2011.

    K ikin da 11.08. 16.08.2011

    Pancevo 17.08. 22.08.2011

    Vrs ac , 06.09-11.09.2011.

    Bor, 13.09. 18.09.2011.

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    Some topics are of particular concern to many European citizens. One of these

    is air quality. This is also one of the areas in which Europe has been mostactive in recent years.

    The European Commission has aimed to develop an overall strategy. MemberStates are required to transpose and implement new directives on air qualitywhich set long-term quality objectives. But it is also our direct responsibility

    to cope with this problem, changing our day by day behavior.

    Like the availability of capital, manpower, or transport infrastructure, thequality of air is likely to become a determining factor in the location ofinvestment and therefore economic growth of a region.

    The way in which not only cities, but also companies, organize their transportsystems will become, without any doubt, one of the major priorities of yearsto come.

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    Pollutant Concentration Averaging period Permitted exceedenceseach year

    Sulphur dioxide (SO2) 350 g/m3 1 hour 24

    125 g/m3 24 hours 3

    Nitrogen dioxide(NO2)

    200 g/m3 1 hour 18

    40 g/m3 1 year n/a

    PM10 50 g/m3 24 hours 35

    Carbon monoxide(CO)

    10 mg/m3 Maximum daily 8 hourmean

    n/a

    Ozone (O3) 120 g/m3 Maximum daily 8 hourmean

    25 days averaged over3 years

    Table 1. EU air quality standards

    *Under the new Directive the member State can apply for an extension of up to five years (i.e. maximum up to2015) in a specific zone. Request is subject to assessment by the Commission. . In such cases within the timeextension period the limit value applies at the level of the limit value + maximum margin of tolerance ( 48g/m3 for annual NO2 limit value).**Under the new Directive the Member State was able to apply for an extension until three years after the dateof entry into force of the new Directive (i.e. May 2011) in a specific zone. Request was subject to assessmentby the Commission. In such cases within the time extension period the limit value applies at the level of thelimit value + maximum margin of tolerance (35 days at 75g/m3 for daily PM10 limit value, 48 g/m3 for

    annual Pm10 limit value).

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    Results of the Air Quality Monitoring Campaign in

    Zrenjanin/Elemir

    Figure 3. Daily mean values recorded for O3, SO2,

    NO, NO2 and NOx in Zrenjanin, location

    Gerontological Center

    Figure 4. Daily mean values recorded for CH4,

    NMHC, THC and CO in Zrenjanin, location

    Gerontological Center

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    Results of the Air Quality Monitoring Campaign in

    Zrenjanin/Elemir

    Figure 5. One minute mean values recorded

    for O3 in Elemir location with AIRPOINTER

    Fig 6. One minute mean values recorded for NO,

    NO2, NOx, SO2 and PM10 in Elemir location with

    AIRPOINTER

    Figure 7. One minute mean values

    recorded for VOC and CO in Elemir

    location with AIRPOINTER

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    Results of the Air Quality Monitoring Campaign in

    Zrenjanin/Elemir

    Conclusions

    An analysis of data recorded by AIRPOINER mobile stations one can conclude:

    the NOx concentrations are low, under 40 g/m3 for one hour mean values

    one episode with relatively high SO2 concentration occurred in 8 August

    the PM10 concentration are low, under 15 g/m3 for daily mean values

    the VOC concentrations around 0.30.5 mg/m3 are low but due to Elemir locationthe composition of those imissions should be further investigated, what kind of VOCs

    are involved? Knowing that benzene concentration in ambient air should not be morethan 5 g/m3 (0.005 mg/m3)

    An analysis of data recorded by UPT mobile stations one can conclude:

    there are no limit excedances for any pollutant

    the NO/NOx and CO recorded concentrations shows the influence of road traffic andvehicle emissions

    SO2 and VOC concentrations also follows the trend of NO/NOx and CO so we canbelieve that they are caused by vehicles and the sulphur content of the fuels used

    The PM10 concentrations are very high, close or above the limit.

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    Results of the Air Quality Monitoring Campaign in

    KIKINDA / BANATSKO VELIKO SELO

    Fig 1. Hourly mean values recorded for NO, NO2,

    NOx, O3, SO2 and PM10 in Kikinda

    Fig 2. Hourly mean values recorded for CO in Kikinda

    Fig 3. Hourly mean values recorded for CO2,

    CH4, NMHC, THC and CO in Banatsko Veliko

    Selo

    Figure 4. Hourly mean values recorded for O3,

    SO2, NO, NO2 and NOx in Banatsko Veliko Selo

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    Results of the Air Quality Monitoring Campaign in

    KIKINDA / BANATSKO VELIKO SELO

    Figure 5. Daily mean values recorded for O3, SO2,

    NO, NO2, NOx and PM10 in Banatsko Veliko Selo

    Figure 6. Daily mean values recorded for CH4, NMHC,

    THC and CO in Banatsko Veliko Selo

    Figure 6. Hourly mean values recorded for PM10 and

    PM2.5 in Banatsko Veliko Selo with Dustrack (light

    scattering)

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    Results of the Air Quality Monitoring Campaign in

    VRSAC

    Fig 1. Hourly mean values recorded for NO, NO2, NOx,

    O3, SO2 in Vrsac at Buss Station, with UPT Mobile

    Laboratory

    Fig 2. Hourly mean values recorded for CO2, CH4,NMHC, THC and CO in Vrsac at Buss Station, with UPT

    Mobile Laboratory

    Fig 3. Hourly mean values recorded for PM10 andPM2.5 in Vrsac at Buss Station with Dustrack (lightscattering), with UPT Mobile Laboratory

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    Fig. 4. Daily mean values recorded for O3, SO2,NO, NO2, NOx and PM10 in Vrsac at BussStation, with UPT Mobile Laboratory

    Fig 5. 3 minute mean values recorded for NOx in Vrsac atMunicipality with AIRPOINTER

    Fig 6. 3 minute mean values recorded for O3 inVrsac at Municipality with AIRPOINTER

    Fig 7. 3 minute mean values recorded for PM10 in Vrsac atMunicipality with AIRPOINTER

    Results of the Air Quality Monitoring Campaign in

    VRSAC

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    Conclus ions

    For the values recorded at VRSAC Main Buss Station we can draw followingconclusions:

    The PM10 concentration is above and/or very close to the EU admissible limit theNO and NO2 concentrations are under the limit but still very high.

    The pics in the graph are caused exclusively by the buss traffic in/out of the

    station. The buss traffic starts at 5:00 AM and stops ~ 11:00 PM with a buss comingin or out every 5 minutes, and a total of more than 100 inputs and outputs everyday.

    CO is under the limit and the variation recorded is following the busses traffic inthe station

    VOC concentrations are high and caused by the fuel combustions. The mistprobable cause is the age of the buses engines giving and incomplete fuelcombustion in the cylinders.

    Ozone concentrations are high but under the admissible limit

    Results of the Air Quality Monitoring Campaign in

    VRSAC

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    Results of the Air Quality Monitoring Campaign in

    PANCEVO

    Fig 1. Hourly mean values recorded for NO, NO2, NOx, O3,

    SO2 in Pancevo, with UPT Mobile Laboratory

    Fig 2. 10 seconds instantaneous values recorded for

    NMHC (VOC) in Pancevo, with UPT Mobile Laboratory

    Fig 3. Hourly mean values recorded for CO2, CH4, NMHC,

    THC and CO in Pancevo, with UPT Mobile LaboratoryFig. 4. Daily mean values recorded for O3, SO2, NO, NO2,

    NOx and PM10 in Pancevo, with UPT Mobile Laboratory

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    Results of the Air Quality Monitoring Campaign in

    PANCEVO

    Figure 5. Daily mean values recorded for CH4, NMHC, THC

    and CO in Pancevo, with UPT Mobile Laboratory

    Figure 6. Hourly mean values recorded for PM10 and PM2.5

    in Pancevo with UPT Mobile Laboratory

    Fig 7. Hourly mean values recorded for NO, NO2, NOx,

    O3, SO2 in Pancevo, with AIRPOINTER

    Fig 8. Hourly mean values recorded for CO in Pancevo,

    with AIRPOINTER

    R l f h Ai Q li M i i C i i

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    Results of the Air Quality Monitoring Campaign in

    BOR/KRIVELJ

    Fig 1. Hourly mean values recorded for CO2, CH4, NMHC, THC

    and CO in BOR, with UPT Mobile LaboratoryFig 2. Hourly mean values recorded for O3

    Fig 3. Hourly mean values recorded for O3 in Bor with

    AIRPOINTER

    Fig 4. Hourly mean values recorded for NO, NO2, NOx, O3,

    SO2 in Bor with AIRPOINTER

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    Results of the Air Quality Monitoring Campaign in

    BOR/KRIVELJ

    Fig 5. Hourly mean values recorded for PM10 in Bor with

    AIRPOINTERFig 6. Instantaneous SO2 concentration recorded for SO2 in

    Bor with AIRPOINTER

    Fig 7. Hourly mean values recorded for SO2 in Bor withAIRPOINTER

    R lt f th Ai Q lit M it i C i i

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    Results of the Air Quality Monitoring Campaign in

    BOR/KRIVELJ

    Conclusions

    Ozone concentrations are high, but under the admissible limit

    NO/NO2/NOx pointed one episodes with high concentrations (14.September), butunder the admissible limit

    The PM10 concentration is above and/or very close to the EU admissible limit, under65 g/m3 for daily mean values

    SO2 concentrations are high. 14th September is the concentration of SO2 was veryhigh at the 730 g/m3. This ``pic`` was recorded about 11 hours. The highest

    concentrations of SO2 on a daily basis is measured by the 340 g/m3.The location where the equipment was placed for monitoring during this period ofmeasurement did not have the best weather conditions for measurement, susceptibleto the wind direction was the opposite direction from where there were measured bythe station, or SO2 concentration was dramatically higher in the city. In this case, theconcentration of SO2 in Krivelj was very high.