Characteristics of Gas Phase Carbonyl Emission and Excess Risk from Incense Stick Burning

Abstract Incense stick burning is one of casual household activity, especially in East and Southeast Asian countries, including Vietnam. In this study, nine incense stick types were collected from Vietnam and investigated the carbonyl emission profile. The result showed that in ten analyzed carbonyl...
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Autor*in:	Chinh, Nguyen Nhu Bao [verfasserIn] Fujii, Yusuke [verfasserIn] Hien, To Thi [verfasserIn] Takenaka, Norimichi [verfasserIn]

Format:	E-Artikel
Sprache:	Englisch

Erschienen:	2020

Schlagwörter:	Carbonyls Incense stick Emission Health risk

Übergeordnetes Werk:	Enthalten in: Water, air & soil pollution - Dordrecht [u.a.] : Springer Science + Business Media B.V, 1971, 231(2020), 6 vom: 08. Juni
Übergeordnetes Werk:	volume:231 ; year:2020 ; number:6 ; day:08 ; month:06

Links:	Volltext

DOI / URN:	10.1007/s11270-020-04674-z

Katalog-ID:	SPR039977080

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520			\|a Abstract Incense stick burning is one of casual household activity, especially in East and Southeast Asian countries, including Vietnam. In this study, nine incense stick types were collected from Vietnam and investigated the carbonyl emission profile. The result showed that in ten analyzed carbonyl compounds, propionaldehyde (3–84%, avg. 32%), acetaldehyde (8–90%, avg. 30%), and acetone (0–38%, avg. 9%) were the most abundant in terms of total weight emitted carbonyls, respectively. The fourth abundant aldehyde was HCHO (1–26%, avg. 8%). The concentration of formaldehyde (HCHO) in released smoke ranged from 46.65 ± 4.44 to 596.89 ± 279.17 μg/$ m^{3} $ (38.02 ± 3.62 to 486.46 ± 242.19 ppb). High concentration of these carbonyls can pose health risk. Therefore, the personal risk assessment of HCHO inhalation exposure was carried out by the burning simulation in a small unventilated room. The risk calculation showed that the cancer risk is 1.81 × $ 10^{−5} $, 24% higher than the base risk. However, the risk may be much higher.
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700	1		\|a Fujii, Yusuke \|e verfasserin \|4 aut
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912			\|a GBV_ILN_40
912			\|a GBV_ILN_60
912			\|a GBV_ILN_62
912			\|a GBV_ILN_63
912			\|a GBV_ILN_69
912			\|a GBV_ILN_70
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912			\|a GBV_ILN_95
912			\|a GBV_ILN_100
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912			\|a GBV_ILN_110
912			\|a GBV_ILN_120
912			\|a GBV_ILN_138
912			\|a GBV_ILN_150
912			\|a GBV_ILN_151
912			\|a GBV_ILN_152
912			\|a GBV_ILN_161
912			\|a GBV_ILN_170
912			\|a GBV_ILN_171
912			\|a GBV_ILN_187
912			\|a GBV_ILN_213
912			\|a GBV_ILN_224
912			\|a GBV_ILN_230
912			\|a GBV_ILN_250
912			\|a GBV_ILN_281
912			\|a GBV_ILN_285
912			\|a GBV_ILN_293
912			\|a GBV_ILN_370
912			\|a GBV_ILN_602
912			\|a GBV_ILN_636
912			\|a GBV_ILN_702
912			\|a GBV_ILN_2001
912			\|a GBV_ILN_2003
912			\|a GBV_ILN_2004
912			\|a GBV_ILN_2005
912			\|a GBV_ILN_2006
912			\|a GBV_ILN_2007
912			\|a GBV_ILN_2008
912			\|a GBV_ILN_2009
912			\|a GBV_ILN_2010
912			\|a GBV_ILN_2011
912			\|a GBV_ILN_2014
912			\|a GBV_ILN_2015
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912			\|a GBV_ILN_2021
912			\|a GBV_ILN_2025
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912			\|a GBV_ILN_2031
912			\|a GBV_ILN_2034
912			\|a GBV_ILN_2037
912			\|a GBV_ILN_2038
912			\|a GBV_ILN_2039
912			\|a GBV_ILN_2044
912			\|a GBV_ILN_2048
912			\|a GBV_ILN_2049
912			\|a GBV_ILN_2050
912			\|a GBV_ILN_2055
912			\|a GBV_ILN_2056
912			\|a GBV_ILN_2057
912			\|a GBV_ILN_2059
912			\|a GBV_ILN_2061
912			\|a GBV_ILN_2064
912			\|a GBV_ILN_2065
912			\|a GBV_ILN_2068
912			\|a GBV_ILN_2088
912			\|a GBV_ILN_2093
912			\|a GBV_ILN_2106
912			\|a GBV_ILN_2107
912			\|a GBV_ILN_2108
912			\|a GBV_ILN_2110
912			\|a GBV_ILN_2111
912			\|a GBV_ILN_2112
912			\|a GBV_ILN_2113
912			\|a GBV_ILN_2118
912			\|a GBV_ILN_2122
912			\|a GBV_ILN_2129
912			\|a GBV_ILN_2143
912			\|a GBV_ILN_2144
912			\|a GBV_ILN_2147
912			\|a GBV_ILN_2148
912			\|a GBV_ILN_2152
912			\|a GBV_ILN_2153
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912			\|a GBV_ILN_2190
912			\|a GBV_ILN_2232
912			\|a GBV_ILN_2336
912			\|a GBV_ILN_2360
912			\|a GBV_ILN_2446
912			\|a GBV_ILN_2470
912			\|a GBV_ILN_2472
912			\|a GBV_ILN_2507
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912			\|a GBV_ILN_2548
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912			\|a GBV_ILN_4037
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912			\|a GBV_ILN_4112
912			\|a GBV_ILN_4125
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912			\|a GBV_ILN_4249
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912			\|a GBV_ILN_4306
912			\|a GBV_ILN_4307
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912			\|a GBV_ILN_4326
912			\|a GBV_ILN_4328
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912			\|a GBV_ILN_4334
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Indexfelder

author_variant	n n b c nnb nnbc y f yf t t h tt tth n t nt
matchkey_str	article:15732932:2020----::hrceitcogshscroyeisoadxesikr
hierarchy_sort_str	2020
bklnumber	43.50
publishDate	2020
allfields	10.1007/s11270-020-04674-z doi (DE-627)SPR039977080 (SPR)s11270-020-04674-z-e DE-627 ger DE-627 rakwb eng 333.7 ASE 43.50 bkl Chinh, Nguyen Nhu Bao verfasserin aut Characteristics of Gas Phase Carbonyl Emission and Excess Risk from Incense Stick Burning 2020 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Abstract Incense stick burning is one of casual household activity, especially in East and Southeast Asian countries, including Vietnam. In this study, nine incense stick types were collected from Vietnam and investigated the carbonyl emission profile. The result showed that in ten analyzed carbonyl compounds, propionaldehyde (3–84%, avg. 32%), acetaldehyde (8–90%, avg. 30%), and acetone (0–38%, avg. 9%) were the most abundant in terms of total weight emitted carbonyls, respectively. The fourth abundant aldehyde was HCHO (1–26%, avg. 8%). The concentration of formaldehyde (HCHO) in released smoke ranged from 46.65 ± 4.44 to 596.89 ± 279.17 μg/$ m^{3} $ (38.02 ± 3.62 to 486.46 ± 242.19 ppb). High concentration of these carbonyls can pose health risk. Therefore, the personal risk assessment of HCHO inhalation exposure was carried out by the burning simulation in a small unventilated room. The risk calculation showed that the cancer risk is 1.81 × $ 10^{−5} $, 24% higher than the base risk. However, the risk may be much higher. Carbonyls (dpeaa)DE-He213 Incense stick (dpeaa)DE-He213 Emission (dpeaa)DE-He213 Health risk (dpeaa)DE-He213 Fujii, Yusuke verfasserin aut Hien, To Thi verfasserin aut Takenaka, Norimichi verfasserin aut Enthalten in Water, air & soil pollution Dordrecht [u.a.] : Springer Science + Business Media B.V, 1971 231(2020), 6 vom: 08. Juni (DE-627)271349417 (DE-600)1479824-4 1573-2932 nnns volume:231 year:2020 number:6 day:08 month:06 https://dx.doi.org/10.1007/s11270-020-04674-z lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER SSG-OPC-GGO SSG-OPC-ASE GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_105 GBV_ILN_110 GBV_ILN_120 GBV_ILN_138 GBV_ILN_150 GBV_ILN_151 GBV_ILN_152 GBV_ILN_161 GBV_ILN_170 GBV_ILN_171 GBV_ILN_187 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_281 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_602 GBV_ILN_636 GBV_ILN_702 GBV_ILN_2001 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2006 GBV_ILN_2007 GBV_ILN_2008 GBV_ILN_2009 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2031 GBV_ILN_2034 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2039 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2055 GBV_ILN_2056 GBV_ILN_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2088 GBV_ILN_2093 GBV_ILN_2106 GBV_ILN_2107 GBV_ILN_2108 GBV_ILN_2110 GBV_ILN_2111 GBV_ILN_2112 GBV_ILN_2113 GBV_ILN_2118 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2144 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2188 GBV_ILN_2190 GBV_ILN_2232 GBV_ILN_2336 GBV_ILN_2360 GBV_ILN_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_2548 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4046 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4126 GBV_ILN_4242 GBV_ILN_4246 GBV_ILN_4249 GBV_ILN_4251 GBV_ILN_4305 GBV_ILN_4306 GBV_ILN_4307 GBV_ILN_4313 GBV_ILN_4322 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4325 GBV_ILN_4326 GBV_ILN_4328 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4393 GBV_ILN_4700 43.50 ASE AR 231 2020 6 08 06
spelling	10.1007/s11270-020-04674-z doi (DE-627)SPR039977080 (SPR)s11270-020-04674-z-e DE-627 ger DE-627 rakwb eng 333.7 ASE 43.50 bkl Chinh, Nguyen Nhu Bao verfasserin aut Characteristics of Gas Phase Carbonyl Emission and Excess Risk from Incense Stick Burning 2020 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Abstract Incense stick burning is one of casual household activity, especially in East and Southeast Asian countries, including Vietnam. In this study, nine incense stick types were collected from Vietnam and investigated the carbonyl emission profile. The result showed that in ten analyzed carbonyl compounds, propionaldehyde (3–84%, avg. 32%), acetaldehyde (8–90%, avg. 30%), and acetone (0–38%, avg. 9%) were the most abundant in terms of total weight emitted carbonyls, respectively. The fourth abundant aldehyde was HCHO (1–26%, avg. 8%). The concentration of formaldehyde (HCHO) in released smoke ranged from 46.65 ± 4.44 to 596.89 ± 279.17 μg/$ m^{3} $ (38.02 ± 3.62 to 486.46 ± 242.19 ppb). High concentration of these carbonyls can pose health risk. Therefore, the personal risk assessment of HCHO inhalation exposure was carried out by the burning simulation in a small unventilated room. The risk calculation showed that the cancer risk is 1.81 × $ 10^{−5} $, 24% higher than the base risk. However, the risk may be much higher. Carbonyls (dpeaa)DE-He213 Incense stick (dpeaa)DE-He213 Emission (dpeaa)DE-He213 Health risk (dpeaa)DE-He213 Fujii, Yusuke verfasserin aut Hien, To Thi verfasserin aut Takenaka, Norimichi verfasserin aut Enthalten in Water, air & soil pollution Dordrecht [u.a.] : Springer Science + Business Media B.V, 1971 231(2020), 6 vom: 08. Juni (DE-627)271349417 (DE-600)1479824-4 1573-2932 nnns volume:231 year:2020 number:6 day:08 month:06 https://dx.doi.org/10.1007/s11270-020-04674-z lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER SSG-OPC-GGO SSG-OPC-ASE GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_105 GBV_ILN_110 GBV_ILN_120 GBV_ILN_138 GBV_ILN_150 GBV_ILN_151 GBV_ILN_152 GBV_ILN_161 GBV_ILN_170 GBV_ILN_171 GBV_ILN_187 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_281 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_602 GBV_ILN_636 GBV_ILN_702 GBV_ILN_2001 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2006 GBV_ILN_2007 GBV_ILN_2008 GBV_ILN_2009 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2031 GBV_ILN_2034 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2039 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2055 GBV_ILN_2056 GBV_ILN_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2088 GBV_ILN_2093 GBV_ILN_2106 GBV_ILN_2107 GBV_ILN_2108 GBV_ILN_2110 GBV_ILN_2111 GBV_ILN_2112 GBV_ILN_2113 GBV_ILN_2118 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2144 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2188 GBV_ILN_2190 GBV_ILN_2232 GBV_ILN_2336 GBV_ILN_2360 GBV_ILN_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_2548 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4046 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4126 GBV_ILN_4242 GBV_ILN_4246 GBV_ILN_4249 GBV_ILN_4251 GBV_ILN_4305 GBV_ILN_4306 GBV_ILN_4307 GBV_ILN_4313 GBV_ILN_4322 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4325 GBV_ILN_4326 GBV_ILN_4328 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4393 GBV_ILN_4700 43.50 ASE AR 231 2020 6 08 06
allfields_unstemmed	10.1007/s11270-020-04674-z doi (DE-627)SPR039977080 (SPR)s11270-020-04674-z-e DE-627 ger DE-627 rakwb eng 333.7 ASE 43.50 bkl Chinh, Nguyen Nhu Bao verfasserin aut Characteristics of Gas Phase Carbonyl Emission and Excess Risk from Incense Stick Burning 2020 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Abstract Incense stick burning is one of casual household activity, especially in East and Southeast Asian countries, including Vietnam. In this study, nine incense stick types were collected from Vietnam and investigated the carbonyl emission profile. The result showed that in ten analyzed carbonyl compounds, propionaldehyde (3–84%, avg. 32%), acetaldehyde (8–90%, avg. 30%), and acetone (0–38%, avg. 9%) were the most abundant in terms of total weight emitted carbonyls, respectively. The fourth abundant aldehyde was HCHO (1–26%, avg. 8%). The concentration of formaldehyde (HCHO) in released smoke ranged from 46.65 ± 4.44 to 596.89 ± 279.17 μg/$ m^{3} $ (38.02 ± 3.62 to 486.46 ± 242.19 ppb). High concentration of these carbonyls can pose health risk. Therefore, the personal risk assessment of HCHO inhalation exposure was carried out by the burning simulation in a small unventilated room. The risk calculation showed that the cancer risk is 1.81 × $ 10^{−5} $, 24% higher than the base risk. However, the risk may be much higher. Carbonyls (dpeaa)DE-He213 Incense stick (dpeaa)DE-He213 Emission (dpeaa)DE-He213 Health risk (dpeaa)DE-He213 Fujii, Yusuke verfasserin aut Hien, To Thi verfasserin aut Takenaka, Norimichi verfasserin aut Enthalten in Water, air & soil pollution Dordrecht [u.a.] : Springer Science + Business Media B.V, 1971 231(2020), 6 vom: 08. Juni (DE-627)271349417 (DE-600)1479824-4 1573-2932 nnns volume:231 year:2020 number:6 day:08 month:06 https://dx.doi.org/10.1007/s11270-020-04674-z lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER SSG-OPC-GGO SSG-OPC-ASE GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_105 GBV_ILN_110 GBV_ILN_120 GBV_ILN_138 GBV_ILN_150 GBV_ILN_151 GBV_ILN_152 GBV_ILN_161 GBV_ILN_170 GBV_ILN_171 GBV_ILN_187 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_281 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_602 GBV_ILN_636 GBV_ILN_702 GBV_ILN_2001 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2006 GBV_ILN_2007 GBV_ILN_2008 GBV_ILN_2009 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2031 GBV_ILN_2034 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2039 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2055 GBV_ILN_2056 GBV_ILN_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2088 GBV_ILN_2093 GBV_ILN_2106 GBV_ILN_2107 GBV_ILN_2108 GBV_ILN_2110 GBV_ILN_2111 GBV_ILN_2112 GBV_ILN_2113 GBV_ILN_2118 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2144 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2188 GBV_ILN_2190 GBV_ILN_2232 GBV_ILN_2336 GBV_ILN_2360 GBV_ILN_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_2548 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4046 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4126 GBV_ILN_4242 GBV_ILN_4246 GBV_ILN_4249 GBV_ILN_4251 GBV_ILN_4305 GBV_ILN_4306 GBV_ILN_4307 GBV_ILN_4313 GBV_ILN_4322 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4325 GBV_ILN_4326 GBV_ILN_4328 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4393 GBV_ILN_4700 43.50 ASE AR 231 2020 6 08 06
allfieldsGer	10.1007/s11270-020-04674-z doi (DE-627)SPR039977080 (SPR)s11270-020-04674-z-e DE-627 ger DE-627 rakwb eng 333.7 ASE 43.50 bkl Chinh, Nguyen Nhu Bao verfasserin aut Characteristics of Gas Phase Carbonyl Emission and Excess Risk from Incense Stick Burning 2020 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Abstract Incense stick burning is one of casual household activity, especially in East and Southeast Asian countries, including Vietnam. In this study, nine incense stick types were collected from Vietnam and investigated the carbonyl emission profile. The result showed that in ten analyzed carbonyl compounds, propionaldehyde (3–84%, avg. 32%), acetaldehyde (8–90%, avg. 30%), and acetone (0–38%, avg. 9%) were the most abundant in terms of total weight emitted carbonyls, respectively. The fourth abundant aldehyde was HCHO (1–26%, avg. 8%). The concentration of formaldehyde (HCHO) in released smoke ranged from 46.65 ± 4.44 to 596.89 ± 279.17 μg/$ m^{3} $ (38.02 ± 3.62 to 486.46 ± 242.19 ppb). High concentration of these carbonyls can pose health risk. Therefore, the personal risk assessment of HCHO inhalation exposure was carried out by the burning simulation in a small unventilated room. The risk calculation showed that the cancer risk is 1.81 × $ 10^{−5} $, 24% higher than the base risk. However, the risk may be much higher. Carbonyls (dpeaa)DE-He213 Incense stick (dpeaa)DE-He213 Emission (dpeaa)DE-He213 Health risk (dpeaa)DE-He213 Fujii, Yusuke verfasserin aut Hien, To Thi verfasserin aut Takenaka, Norimichi verfasserin aut Enthalten in Water, air & soil pollution Dordrecht [u.a.] : Springer Science + Business Media B.V, 1971 231(2020), 6 vom: 08. Juni (DE-627)271349417 (DE-600)1479824-4 1573-2932 nnns volume:231 year:2020 number:6 day:08 month:06 https://dx.doi.org/10.1007/s11270-020-04674-z lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER SSG-OPC-GGO SSG-OPC-ASE GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_105 GBV_ILN_110 GBV_ILN_120 GBV_ILN_138 GBV_ILN_150 GBV_ILN_151 GBV_ILN_152 GBV_ILN_161 GBV_ILN_170 GBV_ILN_171 GBV_ILN_187 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_281 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_602 GBV_ILN_636 GBV_ILN_702 GBV_ILN_2001 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2006 GBV_ILN_2007 GBV_ILN_2008 GBV_ILN_2009 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2031 GBV_ILN_2034 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2039 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2055 GBV_ILN_2056 GBV_ILN_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2088 GBV_ILN_2093 GBV_ILN_2106 GBV_ILN_2107 GBV_ILN_2108 GBV_ILN_2110 GBV_ILN_2111 GBV_ILN_2112 GBV_ILN_2113 GBV_ILN_2118 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2144 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2188 GBV_ILN_2190 GBV_ILN_2232 GBV_ILN_2336 GBV_ILN_2360 GBV_ILN_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_2548 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4046 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4126 GBV_ILN_4242 GBV_ILN_4246 GBV_ILN_4249 GBV_ILN_4251 GBV_ILN_4305 GBV_ILN_4306 GBV_ILN_4307 GBV_ILN_4313 GBV_ILN_4322 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4325 GBV_ILN_4326 GBV_ILN_4328 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4393 GBV_ILN_4700 43.50 ASE AR 231 2020 6 08 06
allfieldsSound	10.1007/s11270-020-04674-z doi (DE-627)SPR039977080 (SPR)s11270-020-04674-z-e DE-627 ger DE-627 rakwb eng 333.7 ASE 43.50 bkl Chinh, Nguyen Nhu Bao verfasserin aut Characteristics of Gas Phase Carbonyl Emission and Excess Risk from Incense Stick Burning 2020 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Abstract Incense stick burning is one of casual household activity, especially in East and Southeast Asian countries, including Vietnam. In this study, nine incense stick types were collected from Vietnam and investigated the carbonyl emission profile. The result showed that in ten analyzed carbonyl compounds, propionaldehyde (3–84%, avg. 32%), acetaldehyde (8–90%, avg. 30%), and acetone (0–38%, avg. 9%) were the most abundant in terms of total weight emitted carbonyls, respectively. The fourth abundant aldehyde was HCHO (1–26%, avg. 8%). The concentration of formaldehyde (HCHO) in released smoke ranged from 46.65 ± 4.44 to 596.89 ± 279.17 μg/$ m^{3} $ (38.02 ± 3.62 to 486.46 ± 242.19 ppb). High concentration of these carbonyls can pose health risk. Therefore, the personal risk assessment of HCHO inhalation exposure was carried out by the burning simulation in a small unventilated room. The risk calculation showed that the cancer risk is 1.81 × $ 10^{−5} $, 24% higher than the base risk. However, the risk may be much higher. Carbonyls (dpeaa)DE-He213 Incense stick (dpeaa)DE-He213 Emission (dpeaa)DE-He213 Health risk (dpeaa)DE-He213 Fujii, Yusuke verfasserin aut Hien, To Thi verfasserin aut Takenaka, Norimichi verfasserin aut Enthalten in Water, air & soil pollution Dordrecht [u.a.] : Springer Science + Business Media B.V, 1971 231(2020), 6 vom: 08. Juni (DE-627)271349417 (DE-600)1479824-4 1573-2932 nnns volume:231 year:2020 number:6 day:08 month:06 https://dx.doi.org/10.1007/s11270-020-04674-z lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER SSG-OPC-GGO SSG-OPC-ASE GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_105 GBV_ILN_110 GBV_ILN_120 GBV_ILN_138 GBV_ILN_150 GBV_ILN_151 GBV_ILN_152 GBV_ILN_161 GBV_ILN_170 GBV_ILN_171 GBV_ILN_187 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_281 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_602 GBV_ILN_636 GBV_ILN_702 GBV_ILN_2001 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2006 GBV_ILN_2007 GBV_ILN_2008 GBV_ILN_2009 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2031 GBV_ILN_2034 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2039 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2055 GBV_ILN_2056 GBV_ILN_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2088 GBV_ILN_2093 GBV_ILN_2106 GBV_ILN_2107 GBV_ILN_2108 GBV_ILN_2110 GBV_ILN_2111 GBV_ILN_2112 GBV_ILN_2113 GBV_ILN_2118 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2144 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2188 GBV_ILN_2190 GBV_ILN_2232 GBV_ILN_2336 GBV_ILN_2360 GBV_ILN_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_2548 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4046 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4126 GBV_ILN_4242 GBV_ILN_4246 GBV_ILN_4249 GBV_ILN_4251 GBV_ILN_4305 GBV_ILN_4306 GBV_ILN_4307 GBV_ILN_4313 GBV_ILN_4322 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4325 GBV_ILN_4326 GBV_ILN_4328 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4393 GBV_ILN_4700 43.50 ASE AR 231 2020 6 08 06
language	English
source	Enthalten in Water, air & soil pollution 231(2020), 6 vom: 08. Juni volume:231 year:2020 number:6 day:08 month:06
sourceStr	Enthalten in Water, air & soil pollution 231(2020), 6 vom: 08. Juni volume:231 year:2020 number:6 day:08 month:06
format_phy_str_mv	Article
institution	findex.gbv.de
topic_facet	Carbonyls Incense stick Emission Health risk
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container_title	Water, air & soil pollution
authorswithroles_txt_mv	Chinh, Nguyen Nhu Bao @@aut@@ Fujii, Yusuke @@aut@@ Hien, To Thi @@aut@@ Takenaka, Norimichi @@aut@@
publishDateDaySort_date	2020-06-08T00:00:00Z
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author	Chinh, Nguyen Nhu Bao
spellingShingle	Chinh, Nguyen Nhu Bao ddc 333.7 bkl 43.50 misc Carbonyls misc Incense stick misc Emission misc Health risk Characteristics of Gas Phase Carbonyl Emission and Excess Risk from Incense Stick Burning
authorStr	Chinh, Nguyen Nhu Bao
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topic_title	333.7 ASE 43.50 bkl Characteristics of Gas Phase Carbonyl Emission and Excess Risk from Incense Stick Burning Carbonyls (dpeaa)DE-He213 Incense stick (dpeaa)DE-He213 Emission (dpeaa)DE-He213 Health risk (dpeaa)DE-He213
topic	ddc 333.7 bkl 43.50 misc Carbonyls misc Incense stick misc Emission misc Health risk
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title	Characteristics of Gas Phase Carbonyl Emission and Excess Risk from Incense Stick Burning
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title_full	Characteristics of Gas Phase Carbonyl Emission and Excess Risk from Incense Stick Burning
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author_browse	Chinh, Nguyen Nhu Bao Fujii, Yusuke Hien, To Thi Takenaka, Norimichi
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title_sort	characteristics of gas phase carbonyl emission and excess risk from incense stick burning
title_auth	Characteristics of Gas Phase Carbonyl Emission and Excess Risk from Incense Stick Burning
abstract	Abstract Incense stick burning is one of casual household activity, especially in East and Southeast Asian countries, including Vietnam. In this study, nine incense stick types were collected from Vietnam and investigated the carbonyl emission profile. The result showed that in ten analyzed carbonyl compounds, propionaldehyde (3–84%, avg. 32%), acetaldehyde (8–90%, avg. 30%), and acetone (0–38%, avg. 9%) were the most abundant in terms of total weight emitted carbonyls, respectively. The fourth abundant aldehyde was HCHO (1–26%, avg. 8%). The concentration of formaldehyde (HCHO) in released smoke ranged from 46.65 ± 4.44 to 596.89 ± 279.17 μg/$ m^{3} $ (38.02 ± 3.62 to 486.46 ± 242.19 ppb). High concentration of these carbonyls can pose health risk. Therefore, the personal risk assessment of HCHO inhalation exposure was carried out by the burning simulation in a small unventilated room. The risk calculation showed that the cancer risk is 1.81 × $ 10^{−5} $, 24% higher than the base risk. However, the risk may be much higher.
abstractGer	Abstract Incense stick burning is one of casual household activity, especially in East and Southeast Asian countries, including Vietnam. In this study, nine incense stick types were collected from Vietnam and investigated the carbonyl emission profile. The result showed that in ten analyzed carbonyl compounds, propionaldehyde (3–84%, avg. 32%), acetaldehyde (8–90%, avg. 30%), and acetone (0–38%, avg. 9%) were the most abundant in terms of total weight emitted carbonyls, respectively. The fourth abundant aldehyde was HCHO (1–26%, avg. 8%). The concentration of formaldehyde (HCHO) in released smoke ranged from 46.65 ± 4.44 to 596.89 ± 279.17 μg/$ m^{3} $ (38.02 ± 3.62 to 486.46 ± 242.19 ppb). High concentration of these carbonyls can pose health risk. Therefore, the personal risk assessment of HCHO inhalation exposure was carried out by the burning simulation in a small unventilated room. The risk calculation showed that the cancer risk is 1.81 × $ 10^{−5} $, 24% higher than the base risk. However, the risk may be much higher.
abstract_unstemmed	Abstract Incense stick burning is one of casual household activity, especially in East and Southeast Asian countries, including Vietnam. In this study, nine incense stick types were collected from Vietnam and investigated the carbonyl emission profile. The result showed that in ten analyzed carbonyl compounds, propionaldehyde (3–84%, avg. 32%), acetaldehyde (8–90%, avg. 30%), and acetone (0–38%, avg. 9%) were the most abundant in terms of total weight emitted carbonyls, respectively. The fourth abundant aldehyde was HCHO (1–26%, avg. 8%). The concentration of formaldehyde (HCHO) in released smoke ranged from 46.65 ± 4.44 to 596.89 ± 279.17 μg/$ m^{3} $ (38.02 ± 3.62 to 486.46 ± 242.19 ppb). High concentration of these carbonyls can pose health risk. Therefore, the personal risk assessment of HCHO inhalation exposure was carried out by the burning simulation in a small unventilated room. The risk calculation showed that the cancer risk is 1.81 × $ 10^{−5} $, 24% higher than the base risk. However, the risk may be much higher.
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container_issue	6
title_short	Characteristics of Gas Phase Carbonyl Emission and Excess Risk from Incense Stick Burning
url	https://dx.doi.org/10.1007/s11270-020-04674-z
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author2	Fujii, Yusuke Hien, To Thi Takenaka, Norimichi
author2Str	Fujii, Yusuke Hien, To Thi Takenaka, Norimichi
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doi_str	10.1007/s11270-020-04674-z
up_date	2024-07-04T02:22:41.653Z
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Characteristics of Gas Phase Carbonyl Emission and Excess Risk from Incense Stick Burning

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