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1 o diastereomers of TpRe(CO)(MeIm)(eta(2)-(R)-alpha-pinene).
2 oratory study investigating the oxidation of alpha-pinene.
3 anic aerosol (SOA) produced by ozonolysis of alpha-pinene.
4 ite effects were observed in the case of (-)-alpha-pinene.
5 nhanced binding and rate of oxidation of (+)-alpha-pinene.
6 P450(cam) for the selective oxidation of (+)-alpha-pinene.
7 2)-benzene) has been developed utilizing (R)-alpha-pinene.
8 tion of the two) affected SOA formation from alpha-pinene.
9 lecules (HOMs) are produced by ozonolysis of alpha-pinene.
10 nic material (SOM) produced by ozonolysis of alpha-pinene.
11 om oxidation of ponderosa pine emissions and alpha-pinene.
16 -ocimene (53.81%), R-D-decalactone (12.75%), alpha-pinene (6.43%), n-heptanol (6.27%), beta-phellande
17 one (2) has been developed starting from (S)-alpha-pinene (7), using photooxygenation, oxidation, and
18 , followed by asymmetric hydroboration using alpha-pinene/9-BBN reagents to form the stereoisomeric a
20 rmed from oxidation of organic gases such as alpha-pinene account for a significant portion of total
21 and a total seven selected terpenes that are alpha-pinene, alpha-phellandrene, (+)-3-carene, sabinene
22 uantified were the monoterpenes beta-pinene, alpha-pinene, alpha-thujene, camphene, sabinene, delta-3
23 only mastic oil -which is comprised of 67.7% alpha-pinene and 18.8% myrcene- induced a statistically
25 . communis showed high contents of sabinene, alpha-pinene and beta-myrcene with 19-30%, 12-24% and 9-
27 ys of the atmospherically important terpenes alpha-pinene and beta-pinene are studied using density f
28 na to a mixture of the bicyclic monoterpenes alpha-pinene and beta-pinene induced defense, accumulati
29 from the NO3 oxidation of two monoterpenes (alpha-pinene and beta-pinene) and investigate how they e
31 plored, targeting two medium-polar analytes, alpha-pinene and cis-verbenol in Boswellia sacra tree re
32 rganic compounds, including the monoterpenes alpha-pinene and limonene and the aromatic catechol (ben
35 This work examines these interactions using alpha-pinene and pellet boiler emissions as a model test
36 osols (SOA) resulting from the ozonolysis of alpha-pinene and photooxidation of toluene, redispersed
38 % enhancements in relative SOA yield for the alpha-pinene and toluene systems, respectively, when see
40 mong the most abundant oxidation products of alpha-pinene, and dimethylamine were selected to study t
41 caryophyllene, the monoterpenes linalool and alpha-pinene, and the homoterpene (E)-4,8-dimethyl-1,3,7
42 enerated from two monoterpenes, limonene and alpha-pinene, and two different oxidants, ozone (O3) and
43 produces significant amounts of (+)- and (-)-alpha-pinene, (+)- and (-)-beta-pinene, myrcene and (+)-
44 atmospherically relevant organic coatings of alpha-pinene (AP) SOA on the reactive uptake of trans-be
45 f oil were alpha-Phellandrene, alpha-cymene, alpha-pinene, Apiol, 1,6-Cyclodecodiene, and 1-methyl-5-
46 xygenated derivatives of the monoterpene (+)-alpha-pinene are found in plant essential oils and used
47 bstituted (C10H16) and deuterated (C10H13D3) alpha-pinene are investigated using coupled ion mobility
49 methodology has been evaluated here by using alpha-pinene as the precursor because it is the monoterp
50 e to study SOA formed from the ozonolysis of alpha-pinene at relative humidities (RHs) up to 87% at 2
51 and this was associated with the presence of alpha-pinene, beta-pinene, and camphene in the emissions
52 much higher concentrations of monoterpenes (alpha-pinene, beta-pinene, and camphene) than did S. ter
54 d production of SOA from limonene, isoprene, alpha-pinene, beta-pinene, and toluene by (3)IC* occurs
55 reactions of (3)IC* with limonene, isoprene, alpha-pinene, beta-pinene, and toluene, and an enhanceme
56 sis reactions of four biogenic monoterpenes (alpha-pinene, beta-pinene, D-limonene, Delta(3)-carene)
57 of five monoterpenes and one sesquiterpene (alpha-pinene, beta-pinene, Delta-3-carene, limonene, sab
58 enes such as (-)-limonene, (-)-linalool, (-)-alpha-pinene/beta-pinene or myrcene, in transgenic tobac
60 t studies of particles from the oxidation of alpha-pinene by ozone and NO(3) radicals at room tempera
64 We demonstrate that spin trap adducts with alpha-pinene CIs also form in the gas phase and that the
66 the structure of the spin trap adducts with alpha-pinene CIs, the reaction was tested in solution, a
68 resentative borane reagents derived from (+)-alpha-pinene confirm that the overall stereoselectivity,
70 inene decreased, while the mole fractions of alpha-pinene, d-limonene (R-(+)-limonene), p-cymene, and
71 4-9 monomers and C16-20H24-36O8-14 dimers in alpha-pinene derived secondary organic aerosol (SOA).
78 We used a smog chamber to generate SOA from alpha-pinene, guaiacol, isoprene, tetradecane, and 1,3,5
82 release characteristics of diacetyl and (-)-alpha-pinene in oil-in-water (o/w) emulsions prepared wi
84 of SOA particles formed during ozonolysis of alpha-pinene in the presence of dioctyl phthalate (DOP)
87 The photooxidation products of a mixture of alpha-pinene (initial concentration 191 ppb), 1,3,5-trim
90 posed mechanism of formation of acetone from alpha-pinene, is determined to possess a barrier of 11.6
91 -dihydronaphthalene; 1,2,4-trimethylbenzene; alpha-pinene; isopropyl 2-methylbutanoate; cymene; 2,6-d
92 The ability of methyl-isoeugenol, limonene, alpha-pinene, isovaleric acid, and isosafrole to inhibit
93 ion of the structures of (+)-camphor and (+)-alpha-pinene lead to active-site mutants containing comb
95 ed the highest positive chemotaxis (70-80%), alpha-pinene, limonene and tridecane were intermediate (
96 each plant, five of which were identified as alpha-pinene, limonene, 2-methoxy-3-(1-methylpropyl)-pyr
97 of the aerosol produced, but in the case of alpha-pinene, little organonitrate and no aerosol is for
99 ectly test whether D62-squalane and SOA from alpha-pinene + O3 form a single solution or two separate
100 ents, one material (D62-squalane or SOA from alpha-pinene + O3) was prepared first to serve as surfac
101 ents of the influence of adding a coating of alpha-pinene+O3 SOA onto squalane particles on the OH-in
103 rain first-generation SOA formation from the alpha-pinene + OH reaction and also study SOA formation
104 Both of the alkoxy radicals formed from the alpha-pinene-OH adduct possess a single favored C-C scis
106 lpha-pinene SOA compounds were produced from alpha-pinene oxidation experiments and used for quantita
109 active was the Y96F/V247L mutant, with a (+)-alpha-pinene oxidation rate of 270 nmol (nmol of P450(ca
111 these studies that the lack of reactivity of alpha-pinene oxide and exo-2,3-epoxynorbornane toward co
112 ) on relative SOA yield and composition from alpha-pinene ozonolysis and the photooxidation of toluen
113 equilibration time scales of SOA formed from alpha-pinene ozonolysis by measuring the dynamic respons
114 H reaction and also study SOA formation from alpha-pinene ozonolysis carried out without an OH scaven
115 ficients of a suite of oxidation products of alpha-pinene ozonolysis in an aerosol that is assumed to
116 e water-soluble component of SOM produced by alpha-pinene ozonolysis is quantified for 20- to 50-mum
117 anic peroxides, which are highly abundant in alpha-pinene ozonolysis SOA (22 +/- 5% by weight), have
118 stripping volatile compounds and ozone from alpha-pinene ozonolysis SOA with three 1-m-long denuders
121 s that describe the partitioning of SOA from alpha-pinene ozonolysis using measurements from a dual-t
122 this end, aerosol chamber investigations of alpha-pinene ozonolysis were conducted under near enviro
124 osol (SOA), formed in a flow tube reactor by alpha-pinene ozonolysis, was studied by passing the fres
127 condary organic aerosol (SOA) formation from alpha-pinene photo-oxidation was studied under atmospher
129 those formed by condensation of the oxidized alpha-pinene products on size-selected DOP particles and
130 ggest that organic peroxy radicals formed by alpha-pinene reacting with secondary OH from ozonolysis
131 OA mass loadings are produced during the NO3+alpha-pinene reaction, during which only 5 highly oxygen
132 s and was proposed in previous studies as an alpha-pinene-related marker compound that is associated
139 of the particle-phase ON evaporates from the alpha-pinene SOA during photochemical aging, thus exhibi
142 emoved, it takes approximately 24 h for pure alpha-pinene SOA particles to evaporate 75% of their mas
145 rylic acid epoxide (MAE)-derived SOA tracer, alpha-pinene SOA tracers, and a biomass burning tracer (
149 ions between ozonolysis reaction products of alpha-pinene, such as pinonaldehyde or pinonic acid, and
152 lly among the different BVOCs, from zero for alpha-pinene to 38-65% for Delta-3-carene and 86% for be
153 and a crotyl borane reagent derived from (-)-alpha-pinene to set both stereocenters in a single step
155 The observed range of relative yields for alpha-pinene, toluene, and acetylene SOA on deliquesced
156 oxidation of VOCs, in particular the terpene alpha-pinene, under atmospherically relevant conditions
158 ysis of human P450 2B6 interactions with (+)-alpha-pinene was undertaken to elucidate the basis of th
159 of decreasing mole fraction was observed in alpha-pinene where growth of d-limonene, p-cymene, and c
160 by the pellet boiler reduced SOA yields from alpha-pinene, whereas the chemical properties of the pri
161 unds by selective enzymatic oxidation of (+)-alpha-pinene, which is readily available in large quanti
162 ilable, enantiomerically pure (1R)- and (1S)-alpha-pinene, which was functionalized and subsequently
163 ) can be obtained with >99% ee starting from alpha-pinene with 80-90% ee by hydroboration using DMAP.
164 vely, J. oxycedrus was strongly dominated by alpha-pinene with 85-92% in both needles and berries.
166 stability, was observed for beta-pinene and alpha-pinene, with growth of d-limonene, p-cymene, and c
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