measurements of nitrogen and sulfur dioxide using passive sampler over 12  months in samsun , turkey , are compared with so2 and no2 concentrations obtained from a co - located chemiluminescence analyzer .
the concentrations of sulfur and nitrogen dioxide in the ambient air during the period from november 2009 to september 2010 are analyzed .
the highest value for annual no2 and so2 averages of passive sampler was 29.65  g / m and 21.01  g / m for exposures of 2-weeks at an industrial site .
the maximum monthly concentration for so2 was observed at the 10 measurement station with 44.19  g / m for august .
the maximum monthly concentration for no2 was observed on the 3 measurement station with 42.83  g / m for november . a negative correlation between nitrogen dioxide concentrations and temperature ( r  =  0.5489 ) was estimated .
a positive correlation between nitrogen dioxide measurement with passive sampler and continuous measurement ( r  =  0.6571 ) was estimated .
industrial establishments operating in the samsun industrial zone for years , activities of the mobile power plants opened but then closed down and natural gas combined cycle plant scheduled to be reactivated require detailed studies of the region in terms of air pollution .
the readings of the measurements made with uninterrupted system measurement devices at one single location revealed that the limit values of the european union were exceeded seasonally in terms of nitrogen dioxide .
however sulfur dioxide values did not exceed national and international legislations in any period ( see table  1 ) .
national and international ambient air quality standards for so 
 2 
 and no 
 2 
 ( as ppb ) in the first instance the passive sampler was developed in america as an on - person air sampler by palmes et al .
( 1976 ) , it ensures that gas or vapor on the atmosphere is carried by molecular diffusion with a physical process and kept in a membrane . here
, the effective power is concentration change between the absorption surface and the air surrounding it and the amount of diffusion occurred is given on 1 fick rule on equation ( 1 ) .(1)f=d.dc / dl where ; f is the molar flux ( g.cm.min ) , d is the diffusion coefficient ( cm / min ) , c is the concentration ( g.cm ) , and l is the diffusion path ( cm ) .
the contaminant concentration kept in the passive sampler depends of the period of atmosphere exposure , quantity of total gas transfer collected in the passive sampler tube , geometric structure of the tube and diffusion coefficient , ambient temperature , ambient humidity , sorbent strength and face velocity .
passive sampler is a preferred method since it does not require power supply , has cost - efficient investment , light , simple analysis procedure as well as not requiring calibration , and suitable for simultaneous multipoint measurement of ambient air pollution .
passive samplers are extremely useful to assess long - term concentration trends ( e.g. , yearly ) and are small , light , re - usable , and soundless . nitrogen dioxide has an irritant effect on the respiratory organs , and long exposures can increasingly lead to airway disorders , such as chronic bronchitis .
the major health impact of sulfur dioxide include effects on breathing , respiratory illness , weakness of lung defenses , increase in the effects of existing respiratory and cardiovascular disease , and death .
explanations of effects of pressure , temperature , and wind speed on the samplers for no2 and so2 have been reported , .
diffusive sampling can be used if the average , instead of the real - time , pollutant concentration is adequate for the purpose of monitoring .
the measurements took place at an industrial zone located in samsun tekkekoy district , selyeri locality .
the area is enclosed in the north by the black sea . the area is also crossed by one of the main samsun and turkey highways , the d010 ( figure  1 , yellow line ) .
the industrial zone digital map of samsun tekkekoy district , scale 1:50000 , is used at the gis - software arcgis ( version 9.2 , esri , ca , usa ) .
the measurement results were introduced in the esri geographic information system software arcgis and the extension geostatistical analyst was used to obtain distribution maps .
the geostatistical analyst , an extension to arcgis , a product of the environmental systems research institute ( esri ) , california , usa , can be applied to analyze the data from air quality monitoring networks and to generate maps of spatial distribution of the monitored air pollutants .
for the pilot study , there were 10 samplers available for field sampling and the sampling area was approximately 20  km ; therefore ; samplers were distributed through background locations only using a systematic grid of 11 km , as can be seen in figure  1 .
the samplers of site were identified and tracked using a global positioning system ( magellan mobile mapper tm6 ) .
measurement points and coordinates the passive samplers used for the measurements are from english gradko company and the technical specifications are explained in detail on table  3 .
the analysis of nitrogen dioxide and sulfur dioxide passive samplers were conducted at gradko s laboratory in england .
all air analyses have been all conducted by ukas accredited methods , working to iso 17025 .
the calibration of sampling tubes was made with gradko environmental laboratory accredited by united kingdom accreditation service ( ukas ) .
the concentrations of nitrite ions and hence no2 chemically adsorbed ( the grid made of stainless steel impregnated with 20% triethanolamine ) are quantitatively determined by uv / visible spectrophotometry ( camspec m550 spectrophotometer ) with reference to a calibration curve derived from the analysis of standard nitrite solutions ( ukas accredited methods ) which is measured colorimetrical .
likewise , for the sulfur dioxide analysis , the grid made of stainless steel impregnated with potassium hydroxide was extracted and then measured with dionex ic 3000 ion chromatography .
determined by an overall m.o.u of 14.081% + / and a limit of detection of 0.026  g  s for sulfur dioxide . determined by an overall m.o.u of 10.907% + / and a limit of detection of 0.021  g no2 for nitrogen dioxide .
properties of passive samplers in order to compare passive samplers with the results of uninterrupted system measurement method operated with chemical optical spectroscopic methods , the data of the measurement station owned by the ministry of environment and forestry was used ( station no.3 ) .
the station no.3 where the reference method chemiluminescence and uv fluorescence method for automatic measurement of no2 and so2 concentrations and are in use .
an automatic ambient so2 analyzer ( af22 m , environnement s.a , france ) and a ambient no2 analyzer ( ac32 m , environnement s.a , france ) were used to measure the average concentrations of sulfur dioxide and nitrogen dioxide . the fixed measurement station data was obtained from air quality monitoring network database .
the data were compiled as 14-day average data and then compared with the passive sampler readings .
the passive samplers were located far from walls and 2.0  m above the ground .
while selecting the locations of passive samplers used for the measurements , several particulars were taken into consideration such as ; exactly determining the industrial contamination in the region , taking into consideration the impact areas by bearing in mind the dominant wind direction , taking into consideration the impacts of significant point contaminants , preventing the impact of pollution caused by vehicles , minimizing the intervention on parks and of wind , comparing the results with uninterrupted measurement system and ensuring ease and safety of passive sampler installation .
the measurement readings obtained for nitrogen dioxide and sulfur dioxide from all measurement stations are given separately on figures  2 and 3 , and seasonal variation of sulfur dioxide and nitrogen dioxide for all stations on figures  4 and 5 .
the highest average concentrations were in winter for nitrogen dioxide and sulphur dioxide ( figures  4 and 5 ) .
the values of so 
 2 
 and no 
 2 
 for 1  5 stations . the values of so 
 2 
 and no 
 2 
 for 6  10 stations .
when a digital map of the readings regarding monthly averages of sulfur dioxide measurements between october 2009 and october 2010 was formed by using arcgis software , it was observed that the values obtained in august 2009 were the highest and reached up to 154.49  g / m ( figure  6 ) . as for the sulfur dioxide ; the overall result observation the digital maps prepared by using arcgis software was that the level of pollution at measurement locations number 1 , 2 , 3 , 4 , 5 and 10 , in other words on the south - west and north - west of the region , is higher .
results of measurement of averaga sulfur dioxide for august 2010 ( as the highest mount ) . according to the measurement readings calculated for nitrogen dioxide
, the highest no2 values reached up to 43.27  g / m in november 2009 ( figure  7 ) .
results of measurement of average nitrogen dioxide for november 2009 ( as the highest mount ) .
g / m and 21.01  g / m for so2 ( figure  8) . dispersion of annual average no 
 2 
 and so 
 2 
 pollutants in samsun in 20092010 . in order to compare the results obtained with passive sampler method with the measurements made with uninterrupted measurement devices ,
passive samplers were located at the fixed measurement station of ministry of forestry and water works , namely sampling station number 3 .
the measurement readings were obtained from air quality monitoring network web page as the reference method of chemiluminescence .
the arithmetical averages of the 14-day exposure period of the passive samplers were calculated by taking into consideration the daily arithmetical averages of the values .
the results of sulfur dioxide and nitrogen dioxide according to two measurement methods so compared are given on figure  8 .
statistically , regression analysis carried out to show the degree of correlation between the continuous monitor and the diffusion tubes gave different regression coefficients .
correlation analysis between passive samplers and the continuous monitor ( figure  9 ) gave a correlation coefficient ( r ) of value . according to the uninterrupted system and passive sampler methods used at measurement station number 3
, there is a low - level relationship in terms of sulfur dioxide measurement methods ( r  =  0.1827 ) but the relation in terms of nitrogen dioxide measurements is confirmed to be r  =  0.6571 ( figure  9 ) .
correlation of passive sampler with continous monitor for so 
 2 
 ve no 
 2 . 
 
box - plots of yearly concentrations of so2 and no2 measured at the sampling points are given in figure  10 .
each vertical box covers 50% of the measured values between the lower and highest quartiles .
the horizontal line inside the box and the cross represent the median and mean values .
no2 can be seen in figure  10 to be associated with significantly higher pollution concentrations than so2 .
the measurement readings were interpreted according to the data obtained from aramba airport meteorology station which is the closest one to the region .
the coordinates of aramba airport meteorology station are 4115'23.92 " n and 3633'23.74 " w , and the distance to the closest measurement locations , namely 6 and 8 , is approximately 5.5 kilometers .
the measurement data obtained by the station on the measurement dates are given on table  4 and the wind rose is given on figure  11 .
the wind rose show that the dominant directions of surface wind in caramba during period of measurement is s. at a typical meteorological condition of average wind speed 2.8 - 3.2  m / s .
samsun aramba airport meteorology station inputs ( october , 2009 - september 2010 ) values of daily average wind rose between of october 2009 with september 2010 in aramba air port meteorology stations .
the correlation between no2 and so2 concentrations and meteorological parameters like air temperature , wind speed , and relative humidity was also calculated for the caramba airport meteorology station .
the other parameters ( wind speed , wind direction , and relative humidity ) is a bad correlation of no2 and so2 , which plays an important role in the distance from the meteorology station .
therefore , the results of correlation of wind speed , wind direction and relative humidity correlation had not been given in here .
the uninterrupted measurement station values and passive sampler readings are compared at the measurement station of the ministry of forestry and water works . a correlation of 69.24%
according to this correlation , the annual nitrogen dioxide average is calculated as 42.36  g / m .
however , as mentioned on the literature , meteorological parameters have significant impact on the correlation and it was not possible to make meteorological measurements at the measurement location during this study .
when the digital map regarding the nitrogen dioxide measurements are reviewed , it is observed that the highest level of pollution is at measurement station of station no.3 and expands around from that location . besides , the nitrogen dioxide values of the measurement point number 5 at yesilyurt port administration vary between 26 to 29  g / m .
it is observed that the nitrogen dioxide is intensified at locations 1 , 2 , 5 and 10 on the west side , starting from measurement station number 3 and expanded towards the black sea from location 5 or towards the inner regions of tekkekoy from location 3 .
4 . when the passive samplers are compared with uninterrupted measurement results at the measurement location number 3 , in terms of sulfur dioxide , a correlation could not be established .
since the results obtained from both passive samplers and uninterrupted measurements are significantly low , we should consider the possibility of errors arising from factors having an impact on sulfur dioxide measurements and devices used .
the reason for this , the sulfur dioxide concentration effected not only passive sampler measurements but also meteorological parameters .
it is observed that the sulfur dioxide distribution heads from south to north - west , towards the black sea from measurement station number 5 .
this work was financed by a scholarship of the ondokuz mays university for support of scientific research ( project no .
the author thank to assistant professor aziz iman , assistant professor nevzat beyazt , and serkan cengel for preparing of digital mapping .
, blacksea agricultural research institute , milangaz , ulusoy maritime high school , tekkeky municipality , and yeilyurt company .
 backgroundmeasurements of nitrogen and sulfur dioxide using passive sampler over 12  months in samsun , turkey , are compared with so2 and no2 concentrations obtained from a co - located chemiluminescence analyzer . 
 the concentrations of sulfur and nitrogen dioxide in the ambient air during the period from november 2009 to september 2010 are analyzed.resultsthe highest value for annual no2 and so2 averages of passive sampler was 29.65  g / m3 and 21.01  g / m3 for exposures of 2-weeks at an industrial site . 
 the maximum monthly concentration for so2 was observed at the 10th measurement station with 44.19  g / m3 for august . 
 the maximum monthly concentration for no2 was observed on the 3rd measurement station with 42.83  g / m3 for november . a negative correlation between nitrogen dioxide concentrations and temperature ( r2  =  0.5489 ) was estimated . 
 a positive correlation between nitrogen dioxide measurement with passive sampler and continuous measurement ( r2  =  0.6571 ) was estimated . 