Decomposition of terpenes by ozone during sampling on Tenax

被引:129
作者
Calogirou, A [1 ]
Larsen, BR [1 ]
Brussol, C [1 ]
Duane, M [1 ]
Kotzias, D [1 ]
机构
[1] COMMISS EUROPEAN COMMUNITIES,JOINT RES CTR,ISPRA ESTAB,INST ENVIRONM,I-21020 ISPRA,ITALY
关键词
D O I
10.1021/ac950803i
中图分类号
O65 [分析化学];
学科分类号
070302 ; 081704 ;
摘要
The ozonolytic decomposition of terpenes and terpenoids during sampling on Tenax is investigated in an artificial air system at ambient concentration levels, The detrimental effect of 8-150 ppbv ozone depends on the chemical structure of the compounds: saturated terpenoids such as 1,8-cineole, camphor, and bornyl acetate are unaffected by ozone, The terpenes and terpenoids which containing one C-C double bond are slightly decomposed in the order camphene < beta-pinene approximate to myrtenal < alpha-pinene < sabinene approximate to citronellal. The compounds containing two or more double bonds are significantly decomposed in the order d-limonene approximate to citral < linalool < beta-ocimene < terpinolene << alpha-terpinene approximate to beta-caryophyllene. For alpha-pinene, sabinene and d-limonene, their ozonolysis products are found on the tubes: pinonaldehyde, 5-(1-methylethyl)bicyclo[3.1.0]hexan-2-one, and 3-(1-methylethenyl)-6-oxoheptanal. The analytical recoveries are significantly enhanced for many compounds when the sampling duration is reduced from 10 min to 30 s, explained by the time available for ozonolysis, A miniature ozone scrubber with multiple layers of MnO2-coated copper nets was developed and thoroughly tested, The optimal number of plies is found to be 8, which ensures quantitative recoveries for all test compounds except alpha-terpinene, beta-caryophyllene, citral, and citronellal. The results that are reported here call into question previous data on terpenes and terpenoids and/or their oxidation products where measurements have been carried out without the prior removal of ozone.
引用
收藏
页码:1499 / 1506
页数:8
相关论文
共 33 条
[1]  
[Anonymous], 2001, GEOCHIM COSMOCHIM AC, DOI DOI 10.1016/S0016-7037(01)00630-5
[2]   RATE CONSTANTS FOR THE GAS-PHASE REACTIONS OF O-3 WITH A SERIES OF MONOTERPENES AND RELATED-COMPOUNDS AT 296-K +/-2-K [J].
ATKINSON, R ;
HASEGAWA, D ;
ASCHMANN, SM .
INTERNATIONAL JOURNAL OF CHEMICAL KINETICS, 1990, 22 (08) :871-887
[3]   RATE CONSTANTS FOR THE GAS-PHASE REACTIONS OF OH AND NO3 RADICALS AND O-3 WITH SABINENE AND CAMPHENE AT 296+/-2-K [J].
ATKINSON, R ;
ASCHMANN, SM ;
AREY, J .
ATMOSPHERIC ENVIRONMENT PART A-GENERAL TOPICS, 1990, 24 (10) :2647-2654
[4]   DIURNAL-VARIATION OF MONOTERPENE CONCENTRATIONS IN OPEN-TOP CHAMBERS AND IN THE WELZHEIM FOREST AIR, FRG [J].
BUFLER, U ;
WEGMANN, K .
ATMOSPHERIC ENVIRONMENT PART A-GENERAL TOPICS, 1991, 25 (02) :251-256
[5]   EVALUATION OF CHROMATOGRAPHIC SORBENTS USED IN AIR-POLLUTION STUDIES [J].
BUNCH, JE ;
PELLIZZARI, ED .
JOURNAL OF CHROMATOGRAPHY, 1979, 186 (DEC) :811-829
[6]   ATMOSPHERIC OXIDATION OF LINALOOL [J].
CALOGIROU, A ;
KOTZIAS, D ;
KETTRUP, A .
NATURWISSENSCHAFTEN, 1995, 82 (06) :288-289
[7]   THEORY OF A SCREEN-TYPE DIFFUSION BATTERY [J].
CHENG, YS ;
YEH, HC .
JOURNAL OF AEROSOL SCIENCE, 1980, 11 (03) :313-&
[8]  
CICCIOLI P, 1992, HRC-J HIGH RES CHROM, V15, P75
[9]  
CICCIOLI P, 1984, PHYSICOCHEMICAL BEHA, P62
[10]  
ENDERS G, 1994, EUR COMM BRUSS BELG