Comparison of methods for measuring atmospheric deposition of arsenic, cadmium, nickel and lead

被引:22
作者
Aas, Wenche [1 ]
Alleman, Laurent Y. [2 ]
Bieber, Elke [3 ]
Gladtke, Dieter [4 ]
Houdret, Jean-Luc [2 ]
Karlsson, Vuokko [5 ]
Monies, Christian [6 ]
机构
[1] NILU, Norwegian Inst Air Res, N-2027 Kjeller, Norway
[2] Univ Lille Nord France, Ecole Mines Douai, Dept Chim & Environm, F-59508 Douai, France
[3] Umweltbundesamt UBA, D-63225 Langen, Germany
[4] Landesamt Nat Umwelt & Verbraucherschutz Nordhein, D-45133 Essen, Germany
[5] Finnish Meteorol Inst, FI-00101 Helsinki, Finland
[6] Natl Environm Res Inst, DK-4000 Roskilde, Denmark
来源
JOURNAL OF ENVIRONMENTAL MONITORING | 2009年 / 11卷 / 06期
关键词
ELEMENTS;
D O I
10.1039/b822330k
中图分类号
O65 [分析化学];
学科分类号
070302 ; 081704 ;
摘要
A comprehensive field intercomparison at four different types of European sites (two rural, one urban and one industrial) comparing three different collectors (wet only, bulk and Bergerhoff samplers) was conducted in the framework of the European Committee for Standardization (CEN) to create an European standard for the deposition of the four elements As, Cd, Ni and Pb. The purpose was to determine whether the proposed methods lead to results within the uncertainty required by the EU's daughter directive (70%). The main conclusion is that a different sampling strategy is needed for rural and industrial sites. Thus, the conclusions on uncertainties and sample approach are presented separately for the different approaches. The wet only and bulk collector ("bulk bottle method'') are comparable at wet rural sites where the total deposition arises mainly from precipitation, the expanded uncertainty when comparing these two types of sampler are below 45% for As, Cd and Pb, 67% for Ni. At industrial sites and possibly very dry rural and urban sites it is necessary to use Bergerhoff samplers or a "bulk bottle+funnel method''. It is not possible to address the total deposition estimation with these methods, but they will give the lowest estimate of the total deposition. The expanded uncertainties when comparing the Bergerhoff and the bulk bottle+funnel methods are below 50% for As and Cd, and 63% for Pb. The uncertainty for Ni was not addressed since the bulk bottle+funnel method did not include a full digestion procedure which is necessary for sites with high loads of undissolved metals. The lowest estimate can however be calculated by comparing parallel Bergerhoff samplers where the expanded uncertainty for Ni was 24%. The reproducibility is comparable to the between sampler/method uncertainties. Sampling and sample preparation were proved to be the main factors in the uncertainty budget of deposition measurements.
引用
收藏
页码:1276 / 1283
页数:8
相关论文
共 11 条
[1]  
AAS W, EMEPCCCREPORT42008
[2]  
*CEN, EN149022005 CEN
[3]  
*EMEP, 22008 EMEP
[4]  
*EMEP CCC, 2001, EMEPCCCREPORT195
[5]  
*EU, 2008, DEM EQ AMB AIR MON M
[6]  
*INT STAND ORG, 209882007 ISO
[7]  
*INT STAND ORG, ISO572421994
[8]   Wet and dry deposition fluxes of trace elements in Tokyo Bay [J].
Sakata, Masahiro ;
Tani, Yukinori ;
Takagi, Tomoharu .
ATMOSPHERIC ENVIRONMENT, 2008, 42 (23) :5913-5922
[9]   Testing the Bergerhoff method to determine the bulk deposition loads of 49 elements [J].
Thöni, L ;
Krieg, F ;
Siewers, U .
ATMOSPHERIC ENVIRONMENT, 1999, 33 (02) :337-344
[10]  
*UN ECE, 2004, EBAIRGE12004 UNECE