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In the fine-particle mode (aerodynamic diameter < 1 pm) non-volatile material has been associated with black carbon (BC) and low-volatile organics and, to a lesser extent, with sea salt and mineral dust. This work analyzes nonvolatile particles at the tropospheric research station Melpitz (Germany), combining experimental methods such as a mobility particle-size spectrometer (3-800nm), a thermodenuder operating at 300 °C, a multi-angle absorption photometer (MAAP), and an aerosol mass spectrometer (AMS). The data were collected during two atmospheric field experiments in May-June 2008 as well as February-March 2009. As a basic result, we detected average non-volatile particlevolume fractions of 11 ± 3% (2008) and 17 ± 8% (2009). In both periods, BC was in close linear correlation with the nonvolatile fraction, but not sufficient to quantitatively explain the non-volatile particle mass concentration. Based on the assumption that BC is not altered by the heating process, the non-volatile particle mass fraction could be explained by the sum of black carbon (47% in summer, 59% in winter) and a non-volatile organic contribution estimated as part of the low-volatility oxygenated organic aerosol (LV-OOA) (53% in summer, 41% in winter); the latter was identified from AMS data by factor analysis. Our results suggest that LVOOA was more volatile in summer (May-June 2008) than in winter (February-March 2009) which was linked to a difference in oxidation levels (lower in summer). Although carbonaceous compounds dominated the sub-pm non-volatile particle mass fraction most of the time, a cross-sensitivity to partially volatile aerosol particles of maritime origin could be seen. These marine particles could be distinguished, however from the carbonaceous particles by a characteristic particle volume-size distribution. The paper discusses the uncertainty of the volatility measurements and outlines the possible merits of volatility analysis as part of continuous atmospheric aerosol measurements. [ABSTRACT FROM AUTHOR]

In the course of two field campaigns, sizesegregated particle samples were collected at nine sites in Germany, including traffic, urban, rural, marine and mountain sites. During the chemical characterisation of the samples some of them were found to contain an unknown substance that was later identified as hydroxymethanesulfonic acid (HMSA). HMSA is known to be formed during the reaction of S(IV) (HSO3- or SO32-) with formaldehyde in the aqueous phase. Due to its stability, HMSA can act as a reservoir species for S(IV) in the atmosphere and is therefore of interest for the understanding of atmospheric sulfur chemistry. However, no HMSA data are available for atmospheric particles from central Europe, and even on a worldwide scale data are scarce. Thus, the present study now provides a representative data set with detailed information on HMSA concentrations in size-segregated central European aerosol particles. HMSA mass concentrations in this data set were highly variable: HMSA was found in 224 out of 738 samples (30%), sometimes in high mass concentrations exceeding those of oxalic acid. On average over all 154 impactor runs, 31.5 ngm-3 HMSA was found in PM10, contributing 0.21% to the total mass. The results show that the particle diameter, the sampling location, the sampling season and the air mass origin impact the HMSA mass concentration. Highest concentrations were found in the particle fraction 0.42-1.2 µm, at urban sites, in winter and with eastern (continental) air masses, respectively. The results suggest that HMSA is formed during aging of pollution plumes. A positive correlation of HMSA with sulfate, oxalate and PM is found (R² >0.4). The results furthermore suggest that the fraction of HMSA in PM slightly decreases with increasing pH. [ABSTRACT FROM AUTHOR]

The article focuses on REMO-HAM, a new regional aerosol-climate model based on the regional model REMO which was developed at Max Planck Institute for Meteorology in Hamburg, Germany. It says that HAM predicts the evolution of the aerosol population and their size-distribution and composition. Moreover, the simulation results from the REMO-HAM, when compared with ECHAM5-HAM, show that it can fairly represent the size distribution and measure aerosol concentration.

Five years of PM10 and PM2.5 ambient air measurements at a roadside, an urban, and a regional background site in Leipzig (Germany) were analyzed for violations of the legal PM10 limit value (EC, 1999). The annual mean PM10 concentrations at the three sites were well below the legal threshold of 40 µgm-3 (32.6, 22.0 and 21.7 µgm-3, respectively). At roadside, the daily maximum value of 50 µgm-3 was exceeded on 232 days (13% of all days) in 2005-2009, which led to a violation of the EC directive in three out of five years. We analysed the meteorological factors and local source contributions that eventually led to the exceedances of the daily limit value. As noted in other urban environments before, most exceedance days were observed in the cold season. Exceedance days were most probable under synoptic situations characterised by stagnant winds, low temperatures and strong temperature inversions in winter time. However, these extreme situations accounted for only less than half of the exeedance days. We also noticed a significant number of exceedance days that occurred in the cold season under south-westerly winds, and in the warm season in the presence of easterly winds. Our analysis suggests that local as well as regional sources of PM are equally responsible for exceedances days at the roadside site. The conclusion is that a combined effort of local, national and international reduction measures appears most likely to avoid systematic exceedances of the daily limit value in the future. [ABSTRACT FROM AUTHOR]

Size-segregated particle samples were collected using a Berner 5-stage impactor (stages 1-5: 0.05-0.14-0.42-1.2-3.5-10 μm aerodynamic diameter). The means for all 169 days and for different categories of days were used for a characterization. The sorting criteria were (a) the distinction between winter (Wi, November to April) and summer (Su, May to October), (b) the distinction between air mass inflow from a sector West (W, 210 °-320 °) and from a sector East (E, 35 °-140 °). For the assignment of the air mass origin 96-h backward trajectories were used and four categories (WiW, WiE, SuW and SuE) with 48, 18, 42 and 29 days were established. The lowest mean particle mass concentrations were found for SuW and the highest for WiE with relative mass concentration distributions of 5.9, 28.2, 36.5, 18.0, and 11.4 % and 3.5, 22.7, 52.6, 16.7, and 4.5 % for stages 1-5, respectively. The mass closure for water soluble ions, water, organic material (OM) and elemental carbon (EC) accounts for 81-99 % of the gravimetric mass in Wi and for 60-81 % for Su, depending on the stage. The fractions of nitrate were relatively high for WiW while sulphate fractions are high for WiE. The estimated concentrations of secondary organic carbon (SOA) on stage 3 for WiW, WiE, SuW and SuE were 0.32, 1.25, 0.27 and 0.58 μgm³, respectively. The highest amount of SOA is found for WiE, representing 59 % of organic carbon (OC). The highest difference in the percentages of SOA in OC was found between winter (WiW 55 %, WiE 59 %) and summer (SuW and SuE 74 %) indicating photochemical processes during long-range transport. The mean Carbon Preference Indices (CPI) are highest for SuE (stage 4: 7.57 and stage 5: 9.82) resulting mainly from plant wax abrasion in the surrounding forests. For WiE the mean PAH concentration on stage 3 (9.7 ngm) is about five times higher than for WiW, indicating long range transport following domestic heating and other combustion processes. [ABSTRACT FROM AUTHOR]

The fractions of local traffic (LT), urban background (UBG) and regional background (RBG) of the particle pollution at a traffic-influenced kerbside in Dresden, Germany, were determined by measurements of size-segregated mass concentration, chemical composition and particle size distributions in a network of five measurement stations partly existing and partly set up for this study. Besides the kerbside station, one urban background site and three rural sites were included in the study. Using data from these different sites, the LT, UBG, and RBG contributions were calculated, following the approach of Lenschow et al. (). At the kerbside site, 19% of the total number concentration (Dp = 10-600 nm) could be attributed to the RBG, 15% to the UBG, and 66% to the LT immediately nearby. Particle mass concentrations up to Dp = 420 nm RBG amounts to 68%, UBG to 21%, and LT only to 11%. Highest mass concentrations were observed at all stations in autumn and winter during easterly inflow directions. The local traffic fraction of PM mass at the kerbside station was found to be 30% for westerly inflow, but only 7% for southeasterly inflow due to the dominating transport fraction from up to 80% of the particle mass at this inflow direction. Size-resolved investigation showed the main fractions in both the particle size ranges of Dp = 0.42 to 1.2 and 0.14 to 0.42 μm at all stations. The main components sulphate, ammonium and total carbon showed higher concentrations at south-eastern/eastern inflow in autumn at all stations, while nitrate at the kerbside and urban background site was higher during westerly inflow in winter. The chemical composition at the regional background site at westerly inflow (12% nitrate, 8% sulphate, 11% total carbon) was significantly different from that at easterly inflow (3% nitrate, 15% sulphate, 22% total carbon). The prevailing part of the ionic mass was always found in the fine particle range of Dp = 0.14 to 1.2 μm at all stations. For all inflow directions highest total carbon concentrations were observed at the kerbside station, especially in the ultra-fine size range of Dp = 0.05 to 0.14 μm with up to 30% of the whole carbon. PAH concentrations were always higher at south-eastern/eastern inflow especially during wintertime. Trace metal components and silicon were found mainly in the coarse mode fraction at the kerbside resulting from abrasion or resuspension. [ABSTRACT FROM AUTHOR]

Atmospheric aerosol particle size distributions at a continental background site in Eastern Germany were examined for a one-year period. Particles were classified using a twin differential mobility particle sizer in a size range between 3 and 800 nm. As a novelty, every second measurement of this experiment involved the removal of volatile chemical compounds in a thermodenuder at 300°C. This concept allowed to quantify the number size distribution of nonvolatile particle cores - primarily associated with elemental carbon, and to compare this to the original non-conditioned size distribution. As a byproduct of the volatility analysis, new particles originating from nucleation inside the thermodenuder can be observed, however, overwhelmingly at diameters below 6 nm. Within the measurement uncertainty, every particle down to particle sizes of 15 nm is concluded to contain a non-volatile core. The volume fraction of non-volatile particulate matter (non-conditioned diameter <800 nm) varied between 10 and 30% and was largely consistent with the experimentally determined mass fraction of elemental carbon. The average size of the non-volatile particle cores was estimated as a function of original non-conditioned size using a summation method, which showed that larger particles (>200 nm) contained more non-volatile compounds than smaller particles (<50 nm), thus indicating a significantly different chemical composition. Two alternative air mass classification schemes based on either, synoptic chart analysis (Berliner Wetterkarte) or back trajectories showed that the volume and number fraction of non-volatile cores depended less on air mass than the total particle number concentration. In all air masses, the non-volatile size distributions showed a more and a less volatile ("soot") mode, the latter being located at about 50 nm. During unstable conditions and in maritime air masses, smaller values were observed compared to stable or continental conditions. This reflects the significant emission of non-volatile material over the continent and, depending on atmospheric stratification, increased concentrations at ground level. [ABSTRACT FROM AUTHOR]

For a period of 10 years (1993–2002) daily PM10 samples were collected on quartz filters by a PM10 high-volume sampler (Sierra-Andersen). In addition, since 1995 weekly filter samples of PM10, PM2.5 and since 1999 PM1 filter samples were collected by a low-volume sampler (‘Partisol 2000’, Rupprecht and Patashnik) on Teflon filters at the IfT research station Melpitz (12°56′E, 51°32′N) located in the downwind plume of the Leipzig conurbation in central Europe. The resulting time series were compared based on weekly means (particle mass r=0.90, NO3- mass r=0.94, SO42- mass r=0.92 and NH4+ mass r=0.90) and integrated in a historical mass trend (since 1983) for Saxony. In the data (1983–1990) the total particle mass concentration (TSP) shows big scatter with a mean of about 75μgm-3. Since the re-unification of Germany in 1990 a decrease in PM10-concentration to a mean of 20–30μgm-3 is observed. The mass concentration of PM10 shows a decreasing trend from a yearly maximum value in 1996 (39μgm-3) to a mean value for 1999–2002 of about 23μgm-3. The highest values were observed just before the winter of 1997/1998. No pronounced concentration peaks were found in the following winters. Reasons are the rapid modernization of power plants and the decreasing number of coal heating systems in the Leipzig conurbation and its surroundings as well as a lack of strong inversion situations. The NO3-/SO42--ratio shows a typical increasing trend caused by the decreasing SO42--mass concentration in PM10 which originates in the dramatic decrease of SO2 concentrations. From the weekly low-volume samples the mass contributions of PM1, PM2.5–PM1 and PM10–PM2.5 to PM10 (100%) for 1999–2002 were about 61%, 20% and 19% for winter and 42%, 13% and 45% for summer, respectively. Most of the PM2.5 mass is PM1. During summers the weekly ratio of coarse particles (PM10–PM2.5) to fine particles (PM2.5) was higher (about 1.4) than the winter value (about 0.3). An additional impactor for PM1 at the low-volume sampler contains a quartz filter for the weekly determination of organic carbon (OC) and elemental carbon (EC) using a thermographic method. About 30% of the PM1 mass is total carbon (TC=OC+EC). The percentage of EC to TC seems to be increasing in the summer from 1999 to 2002. [Copyright &y& Elsevier]