Comparison of 7 years of satellite-borne and ground-based tropospheric NO2 measurements around Milan, Italy
Identifieur interne : 000161 ( PascalFrancis/Corpus ); précédent : 000160; suivant : 000162Comparison of 7 years of satellite-borne and ground-based tropospheric NO2 measurements around Milan, Italy
Auteurs : C. Ordonez ; A. Richter ; M. Steinbacher ; C. Zellweger ; H. Nüss ; J. P. Burrows ; A. S. H. PrevotSource :
- Journal of geophysical research [ 0148-0227 ] ; 2006.
Descripteurs français
- Pascal (Inist)
- Satellite, Troposphère, Densité colonne, Monde, Ozone, Surveillance, Etude expérimentale, Absorption optique, Mesure in situ, Nuage, Versant, Automne, Hiver, Source, Printemps, Eté, Peracétique acide nitrate, Nitrique acide, Modèle, Traceur, Coefficient corrélation, Variation spatiale, Pollution, Cycle, Aérosol, Milan.
English descriptors
- KwdEn :
- Autumn, Column density, Measurement in situ, Milan Italy, Nitric acid, Optical absorption, Peroxyacetyl nitrate, Spring(season), Summer, Winter, aerosols, clouds, correlation coefficient, cycles, experimental studies, global, models, monitoring, ozone, pollution, satellites, slopes, spatial variations, springs, tracers, troposphere.
Abstract
Tropospheric NO2 vertical column densities (VCDs) over the Lombardy region were retrieved from measurements of the Global Ozone Monitoring Experiment (GOME) spectrometer for the period 1996-2002 using a differential optical absorption method. This data set was compared with in situ measurements of NO2 at around 100 ground stations in the Lombardy region, northern Italy. The tropospheric NO2 VCDs are reasonably well correlated with the near-surface measurements under cloud-free conditions. However, the slope of the tropospheric VCDs versus ground measurements is higher in autumn-winter than in spring-summer. This effect is clearly reduced when the peroxyacetyl nitrate and nitric acid (HNO3) interferences of conventional NOxanalyzers are taken into account. For a more quantitative comparison, the NO2ground measurements were scaled to tropospheric VCDs using a seasonal NO2 vertical profile over northern Italy calculated by the Model of Ozone and Related Tracers 2 (MOZART-2). The tropospheric VCDs retrieved from satellite and those determined from ground measurements agree well, with a correlation coefficient R = 0.78 and a slope close to 1 for slightly polluted stations. GOME cannot reproduce the high NO2 amounts over the most polluted stations, mainly because of the large spatial variability in the distribution of pollution within the GOME footprint. The yearly and weekly cycles of the tropospheric NO2 VCDs are similar for both data sets, with significantly lower values in the summer months and on Sundays, respectively. Considering the pollution level and high aerosol concentrations of this region, the agreement is very good. Furthermore, uncertainties in the ground-based measurements, including the extrapolation to NO2 VCDs, might be as important as those of the NO2 satellite retrieval itself.
Notice en format standard (ISO 2709)
Pour connaître la documentation sur le format Inist Standard.
pA |
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Format Inist (serveur)
NO : | PASCAL 06-0232377 INIST |
---|---|
ET : | Comparison of 7 years of satellite-borne and ground-based tropospheric NO2 measurements around Milan, Italy |
AU : | ORDONEZ (C.); RICHTER (A.); STEINBACHER (M.); ZELLWEGER (C.); NÜSS (H.); BURROWS (J. P.); PREVOT (A. S. H.) |
AF : | Laboratory of Atmospheric Chemistry, Paul Scherrer Institut/Villigen/Suisse (1 aut., 7 aut.); Institute of Environmental Physics, University of Bremen/Bremen/Allemagne (2 aut., 5 aut., 6 aut.); Swiss Federal Institute for Materials Science and Technology/Dubendorf/Suisse (3 aut., 4 aut.) |
DT : | Publication en série; Niveau analytique |
SO : | Journal of geophysical research; ISSN 0148-0227; Etats-Unis; Da. 2006; Vol. 111; No. D5; D05310.1-D05310.12; Bibl. 1 p.1/4 |
LA : | Anglais |
EA : | Tropospheric NO2 vertical column densities (VCDs) over the Lombardy region were retrieved from measurements of the Global Ozone Monitoring Experiment (GOME) spectrometer for the period 1996-2002 using a differential optical absorption method. This data set was compared with in situ measurements of NO2 at around 100 ground stations in the Lombardy region, northern Italy. The tropospheric NO2 VCDs are reasonably well correlated with the near-surface measurements under cloud-free conditions. However, the slope of the tropospheric VCDs versus ground measurements is higher in autumn-winter than in spring-summer. This effect is clearly reduced when the peroxyacetyl nitrate and nitric acid (HNO3) interferences of conventional NOxanalyzers are taken into account. For a more quantitative comparison, the NO2ground measurements were scaled to tropospheric VCDs using a seasonal NO2 vertical profile over northern Italy calculated by the Model of Ozone and Related Tracers 2 (MOZART-2). The tropospheric VCDs retrieved from satellite and those determined from ground measurements agree well, with a correlation coefficient R = 0.78 and a slope close to 1 for slightly polluted stations. GOME cannot reproduce the high NO2 amounts over the most polluted stations, mainly because of the large spatial variability in the distribution of pollution within the GOME footprint. The yearly and weekly cycles of the tropospheric NO2 VCDs are similar for both data sets, with significantly lower values in the summer months and on Sundays, respectively. Considering the pollution level and high aerosol concentrations of this region, the agreement is very good. Furthermore, uncertainties in the ground-based measurements, including the extrapolation to NO2 VCDs, might be as important as those of the NO2 satellite retrieval itself. |
CC : | 220; 001E; 001E01 |
FD : | Satellite; Troposphère; Densité colonne; Monde; Ozone; Surveillance; Etude expérimentale; Absorption optique; Mesure in situ; Nuage; Versant; Automne; Hiver; Source; Printemps; Eté; Peracétique acide nitrate; Nitrique acide; Modèle; Traceur; Coefficient corrélation; Variation spatiale; Pollution; Cycle; Aérosol; Milan |
FG : | Lombardie; Italie; Europe Sud; Europe |
ED : | satellites; troposphere; Column density; global; ozone; monitoring; experimental studies; Optical absorption; Measurement in situ; clouds; slopes; Autumn; Winter; springs; Spring(season); Summer; Peroxyacetyl nitrate; Nitric acid; models; tracers; correlation coefficient; spatial variations; pollution; cycles; aerosols; Milan Italy |
EG : | Lombardy Italy; Italy; Southern Europe; Europe |
SD : | Satélite; Densidad columna; Mundo; Ozono; Vigilancia; Absorción óptica; Medición en sitio; Nube; Declive; Otoño; Invierno; Fuente; Primavera; Verano; Nítrico ácido; Modelo; Trazador; Coeficiente correlación; Variación espacial; Polución; Aerosol |
LO : | INIST-3144.354000156802760390 |
ID : | 06-0232377 |
Links to Exploration step
Pascal:06-0232377Le document en format XML
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<series><title level="j" type="main">Journal of geophysical research</title>
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<term>Optical absorption</term>
<term>Peroxyacetyl nitrate</term>
<term>Spring(season)</term>
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<term>Troposphère</term>
<term>Densité colonne</term>
<term>Monde</term>
<term>Ozone</term>
<term>Surveillance</term>
<term>Etude expérimentale</term>
<term>Absorption optique</term>
<term>Mesure in situ</term>
<term>Nuage</term>
<term>Versant</term>
<term>Automne</term>
<term>Hiver</term>
<term>Source</term>
<term>Printemps</term>
<term>Eté</term>
<term>Peracétique acide nitrate</term>
<term>Nitrique acide</term>
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<term>Traceur</term>
<term>Coefficient corrélation</term>
<term>Variation spatiale</term>
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<front><div type="abstract" xml:lang="en">Tropospheric NO<sub>2</sub>
vertical column densities (VCDs) over the Lombardy region were retrieved from measurements of the Global Ozone Monitoring Experiment (GOME) spectrometer for the period 1996-2002 using a differential optical absorption method. This data set was compared with in situ measurements of NO<sub>2</sub>
at around 100 ground stations in the Lombardy region, northern Italy. The tropospheric NO<sub>2</sub>
VCDs are reasonably well correlated with the near-surface measurements under cloud-free conditions. However, the slope of the tropospheric VCDs versus ground measurements is higher in autumn-winter than in spring-summer. This effect is clearly reduced when the peroxyacetyl nitrate and nitric acid (HNO<sub>3</sub>
) interferences of conventional NO<sub>x</sub>
analyzers are taken into account. For a more quantitative comparison, the NO<sub>2</sub>
ground measurements were scaled to tropospheric VCDs using a seasonal NO<sub>2</sub>
vertical profile over northern Italy calculated by the Model of Ozone and Related Tracers 2 (MOZART-2). The tropospheric VCDs retrieved from satellite and those determined from ground measurements agree well, with a correlation coefficient R = 0.78 and a slope close to 1 for slightly polluted stations. GOME cannot reproduce the high NO<sub>2</sub>
amounts over the most polluted stations, mainly because of the large spatial variability in the distribution of pollution within the GOME footprint. The yearly and weekly cycles of the tropospheric NO<sub>2</sub>
VCDs are similar for both data sets, with significantly lower values in the summer months and on Sundays, respectively. Considering the pollution level and high aerosol concentrations of this region, the agreement is very good. Furthermore, uncertainties in the ground-based measurements, including the extrapolation to NO<sub>2</sub>
VCDs, might be as important as those of the NO<sub>2</sub>
satellite retrieval itself.</div>
</front>
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<fC01 i1="01" l="ENG"><s0>Tropospheric NO<sub>2</sub>
vertical column densities (VCDs) over the Lombardy region were retrieved from measurements of the Global Ozone Monitoring Experiment (GOME) spectrometer for the period 1996-2002 using a differential optical absorption method. This data set was compared with in situ measurements of NO<sub>2</sub>
at around 100 ground stations in the Lombardy region, northern Italy. The tropospheric NO<sub>2</sub>
VCDs are reasonably well correlated with the near-surface measurements under cloud-free conditions. However, the slope of the tropospheric VCDs versus ground measurements is higher in autumn-winter than in spring-summer. This effect is clearly reduced when the peroxyacetyl nitrate and nitric acid (HNO<sub>3</sub>
) interferences of conventional NO<sub>x</sub>
analyzers are taken into account. For a more quantitative comparison, the NO<sub>2</sub>
ground measurements were scaled to tropospheric VCDs using a seasonal NO<sub>2</sub>
vertical profile over northern Italy calculated by the Model of Ozone and Related Tracers 2 (MOZART-2). The tropospheric VCDs retrieved from satellite and those determined from ground measurements agree well, with a correlation coefficient R = 0.78 and a slope close to 1 for slightly polluted stations. GOME cannot reproduce the high NO<sub>2</sub>
amounts over the most polluted stations, mainly because of the large spatial variability in the distribution of pollution within the GOME footprint. The yearly and weekly cycles of the tropospheric NO<sub>2</sub>
VCDs are similar for both data sets, with significantly lower values in the summer months and on Sundays, respectively. Considering the pollution level and high aerosol concentrations of this region, the agreement is very good. Furthermore, uncertainties in the ground-based measurements, including the extrapolation to NO<sub>2</sub>
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<s5>06</s5>
</fC03>
<fC03 i1="07" i2="2" l="FRE"><s0>Etude expérimentale</s0>
<s5>07</s5>
</fC03>
<fC03 i1="07" i2="2" l="ENG"><s0>experimental studies</s0>
<s5>07</s5>
</fC03>
<fC03 i1="08" i2="X" l="FRE"><s0>Absorption optique</s0>
<s5>08</s5>
</fC03>
<fC03 i1="08" i2="X" l="ENG"><s0>Optical absorption</s0>
<s5>08</s5>
</fC03>
<fC03 i1="08" i2="X" l="SPA"><s0>Absorción óptica</s0>
<s5>08</s5>
</fC03>
<fC03 i1="09" i2="X" l="FRE"><s0>Mesure in situ</s0>
<s5>09</s5>
</fC03>
<fC03 i1="09" i2="X" l="ENG"><s0>Measurement in situ</s0>
<s5>09</s5>
</fC03>
<fC03 i1="09" i2="X" l="SPA"><s0>Medición en sitio</s0>
<s5>09</s5>
</fC03>
<fC03 i1="10" i2="2" l="FRE"><s0>Nuage</s0>
<s5>10</s5>
</fC03>
<fC03 i1="10" i2="2" l="ENG"><s0>clouds</s0>
<s5>10</s5>
</fC03>
<fC03 i1="10" i2="2" l="SPA"><s0>Nube</s0>
<s5>10</s5>
</fC03>
<fC03 i1="11" i2="2" l="FRE"><s0>Versant</s0>
<s5>11</s5>
</fC03>
<fC03 i1="11" i2="2" l="ENG"><s0>slopes</s0>
<s5>11</s5>
</fC03>
<fC03 i1="11" i2="2" l="SPA"><s0>Declive</s0>
<s5>11</s5>
</fC03>
<fC03 i1="12" i2="X" l="FRE"><s0>Automne</s0>
<s5>12</s5>
</fC03>
<fC03 i1="12" i2="X" l="ENG"><s0>Autumn</s0>
<s5>12</s5>
</fC03>
<fC03 i1="12" i2="X" l="SPA"><s0>Otoño</s0>
<s5>12</s5>
</fC03>
<fC03 i1="13" i2="X" l="FRE"><s0>Hiver</s0>
<s5>13</s5>
</fC03>
<fC03 i1="13" i2="X" l="ENG"><s0>Winter</s0>
<s5>13</s5>
</fC03>
<fC03 i1="13" i2="X" l="SPA"><s0>Invierno</s0>
<s5>13</s5>
</fC03>
<fC03 i1="14" i2="2" l="FRE"><s0>Source</s0>
<s5>14</s5>
</fC03>
<fC03 i1="14" i2="2" l="ENG"><s0>springs</s0>
<s5>14</s5>
</fC03>
<fC03 i1="14" i2="2" l="SPA"><s0>Fuente</s0>
<s5>14</s5>
</fC03>
<fC03 i1="15" i2="X" l="FRE"><s0>Printemps</s0>
<s5>15</s5>
</fC03>
<fC03 i1="15" i2="X" l="ENG"><s0>Spring(season)</s0>
<s5>15</s5>
</fC03>
<fC03 i1="15" i2="X" l="SPA"><s0>Primavera</s0>
<s5>15</s5>
</fC03>
<fC03 i1="16" i2="X" l="FRE"><s0>Eté</s0>
<s5>16</s5>
</fC03>
<fC03 i1="16" i2="X" l="ENG"><s0>Summer</s0>
<s5>16</s5>
</fC03>
<fC03 i1="16" i2="X" l="SPA"><s0>Verano</s0>
<s5>16</s5>
</fC03>
<fC03 i1="17" i2="3" l="FRE"><s0>Peracétique acide nitrate</s0>
<s2>NK</s2>
<s5>17</s5>
</fC03>
<fC03 i1="17" i2="3" l="ENG"><s0>Peroxyacetyl nitrate</s0>
<s2>NK</s2>
<s5>17</s5>
</fC03>
<fC03 i1="18" i2="X" l="FRE"><s0>Nitrique acide</s0>
<s2>NK</s2>
<s5>18</s5>
</fC03>
<fC03 i1="18" i2="X" l="ENG"><s0>Nitric acid</s0>
<s2>NK</s2>
<s5>18</s5>
</fC03>
<fC03 i1="18" i2="X" l="SPA"><s0>Nítrico ácido</s0>
<s2>NK</s2>
<s5>18</s5>
</fC03>
<fC03 i1="19" i2="2" l="FRE"><s0>Modèle</s0>
<s5>19</s5>
</fC03>
<fC03 i1="19" i2="2" l="ENG"><s0>models</s0>
<s5>19</s5>
</fC03>
<fC03 i1="19" i2="2" l="SPA"><s0>Modelo</s0>
<s5>19</s5>
</fC03>
<fC03 i1="20" i2="2" l="FRE"><s0>Traceur</s0>
<s5>20</s5>
</fC03>
<fC03 i1="20" i2="2" l="ENG"><s0>tracers</s0>
<s5>20</s5>
</fC03>
<fC03 i1="20" i2="2" l="SPA"><s0>Trazador</s0>
<s5>20</s5>
</fC03>
<fC03 i1="21" i2="2" l="FRE"><s0>Coefficient corrélation</s0>
<s5>21</s5>
</fC03>
<fC03 i1="21" i2="2" l="ENG"><s0>correlation coefficient</s0>
<s5>21</s5>
</fC03>
<fC03 i1="21" i2="2" l="SPA"><s0>Coeficiente correlación</s0>
<s5>21</s5>
</fC03>
<fC03 i1="22" i2="2" l="FRE"><s0>Variation spatiale</s0>
<s5>22</s5>
</fC03>
<fC03 i1="22" i2="2" l="ENG"><s0>spatial variations</s0>
<s5>22</s5>
</fC03>
<fC03 i1="22" i2="2" l="SPA"><s0>Variación espacial</s0>
<s5>22</s5>
</fC03>
<fC03 i1="23" i2="2" l="FRE"><s0>Pollution</s0>
<s5>23</s5>
</fC03>
<fC03 i1="23" i2="2" l="ENG"><s0>pollution</s0>
<s5>23</s5>
</fC03>
<fC03 i1="23" i2="2" l="SPA"><s0>Polución</s0>
<s5>23</s5>
</fC03>
<fC03 i1="24" i2="2" l="FRE"><s0>Cycle</s0>
<s5>24</s5>
</fC03>
<fC03 i1="24" i2="2" l="ENG"><s0>cycles</s0>
<s5>24</s5>
</fC03>
<fC03 i1="25" i2="2" l="FRE"><s0>Aérosol</s0>
<s5>25</s5>
</fC03>
<fC03 i1="25" i2="2" l="ENG"><s0>aerosols</s0>
<s5>25</s5>
</fC03>
<fC03 i1="25" i2="2" l="SPA"><s0>Aerosol</s0>
<s5>25</s5>
</fC03>
<fC03 i1="26" i2="2" l="FRE"><s0>Milan</s0>
<s2>NG</s2>
<s5>61</s5>
</fC03>
<fC03 i1="26" i2="2" l="ENG"><s0>Milan Italy</s0>
<s2>NG</s2>
<s5>61</s5>
</fC03>
<fC07 i1="01" i2="2" l="FRE"><s0>Lombardie</s0>
<s2>NG</s2>
</fC07>
<fC07 i1="01" i2="2" l="ENG"><s0>Lombardy Italy</s0>
<s2>NG</s2>
</fC07>
<fC07 i1="01" i2="2" l="SPA"><s0>Lombardía</s0>
<s2>NG</s2>
</fC07>
<fC07 i1="02" i2="2" l="FRE"><s0>Italie</s0>
<s2>NG</s2>
</fC07>
<fC07 i1="02" i2="2" l="ENG"><s0>Italy</s0>
<s2>NG</s2>
</fC07>
<fC07 i1="02" i2="2" l="SPA"><s0>Italia</s0>
<s2>NG</s2>
</fC07>
<fC07 i1="03" i2="2" l="FRE"><s0>Europe Sud</s0>
<s2>NG</s2>
</fC07>
<fC07 i1="03" i2="2" l="ENG"><s0>Southern Europe</s0>
<s2>NG</s2>
</fC07>
<fC07 i1="03" i2="2" l="SPA"><s0>Europa Sur</s0>
<s2>NG</s2>
</fC07>
<fC07 i1="04" i2="2" l="FRE"><s0>Europe</s0>
</fC07>
<fC07 i1="04" i2="2" l="ENG"><s0>Europe</s0>
</fC07>
<fC07 i1="04" i2="2" l="SPA"><s0>Europa</s0>
</fC07>
<fN21><s1>142</s1>
</fN21>
<fN44 i1="01"><s1>OTO</s1>
</fN44>
<fN82><s1>OTO</s1>
</fN82>
</pA>
</standard>
<server><NO>PASCAL 06-0232377 INIST</NO>
<ET>Comparison of 7 years of satellite-borne and ground-based tropospheric NO<sub>2</sub>
measurements around Milan, Italy</ET>
<AU>ORDONEZ (C.); RICHTER (A.); STEINBACHER (M.); ZELLWEGER (C.); NÜSS (H.); BURROWS (J. P.); PREVOT (A. S. H.)</AU>
<AF>Laboratory of Atmospheric Chemistry, Paul Scherrer Institut/Villigen/Suisse (1 aut., 7 aut.); Institute of Environmental Physics, University of Bremen/Bremen/Allemagne (2 aut., 5 aut., 6 aut.); Swiss Federal Institute for Materials Science and Technology/Dubendorf/Suisse (3 aut., 4 aut.)</AF>
<DT>Publication en série; Niveau analytique</DT>
<SO>Journal of geophysical research; ISSN 0148-0227; Etats-Unis; Da. 2006; Vol. 111; No. D5; D05310.1-D05310.12; Bibl. 1 p.1/4</SO>
<LA>Anglais</LA>
<EA>Tropospheric NO<sub>2</sub>
vertical column densities (VCDs) over the Lombardy region were retrieved from measurements of the Global Ozone Monitoring Experiment (GOME) spectrometer for the period 1996-2002 using a differential optical absorption method. This data set was compared with in situ measurements of NO<sub>2</sub>
at around 100 ground stations in the Lombardy region, northern Italy. The tropospheric NO<sub>2</sub>
VCDs are reasonably well correlated with the near-surface measurements under cloud-free conditions. However, the slope of the tropospheric VCDs versus ground measurements is higher in autumn-winter than in spring-summer. This effect is clearly reduced when the peroxyacetyl nitrate and nitric acid (HNO<sub>3</sub>
) interferences of conventional NO<sub>x</sub>
analyzers are taken into account. For a more quantitative comparison, the NO<sub>2</sub>
ground measurements were scaled to tropospheric VCDs using a seasonal NO<sub>2</sub>
vertical profile over northern Italy calculated by the Model of Ozone and Related Tracers 2 (MOZART-2). The tropospheric VCDs retrieved from satellite and those determined from ground measurements agree well, with a correlation coefficient R = 0.78 and a slope close to 1 for slightly polluted stations. GOME cannot reproduce the high NO<sub>2</sub>
amounts over the most polluted stations, mainly because of the large spatial variability in the distribution of pollution within the GOME footprint. The yearly and weekly cycles of the tropospheric NO<sub>2</sub>
VCDs are similar for both data sets, with significantly lower values in the summer months and on Sundays, respectively. Considering the pollution level and high aerosol concentrations of this region, the agreement is very good. Furthermore, uncertainties in the ground-based measurements, including the extrapolation to NO<sub>2</sub>
VCDs, might be as important as those of the NO<sub>2</sub>
satellite retrieval itself.</EA>
<CC>220; 001E; 001E01</CC>
<FD>Satellite; Troposphère; Densité colonne; Monde; Ozone; Surveillance; Etude expérimentale; Absorption optique; Mesure in situ; Nuage; Versant; Automne; Hiver; Source; Printemps; Eté; Peracétique acide nitrate; Nitrique acide; Modèle; Traceur; Coefficient corrélation; Variation spatiale; Pollution; Cycle; Aérosol; Milan</FD>
<FG>Lombardie; Italie; Europe Sud; Europe</FG>
<ED>satellites; troposphere; Column density; global; ozone; monitoring; experimental studies; Optical absorption; Measurement in situ; clouds; slopes; Autumn; Winter; springs; Spring(season); Summer; Peroxyacetyl nitrate; Nitric acid; models; tracers; correlation coefficient; spatial variations; pollution; cycles; aerosols; Milan Italy</ED>
<EG>Lombardy Italy; Italy; Southern Europe; Europe</EG>
<SD>Satélite; Densidad columna; Mundo; Ozono; Vigilancia; Absorción óptica; Medición en sitio; Nube; Declive; Otoño; Invierno; Fuente; Primavera; Verano; Nítrico ácido; Modelo; Trazador; Coeficiente correlación; Variación espacial; Polución; Aerosol</SD>
<LO>INIST-3144.354000156802760390</LO>
<ID>06-0232377</ID>
</server>
</inist>
</record>
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