Linalool Biotransformation
J. Agric. Food Chem., Vol. 56, No. 9, 2008 3289
linalool oxide, 1188; cis-pyranoid linalool oxide, 1195; lilac alcohol
isomer d, 1213; lilac alcohol isomer e, 1230; lilac alcohol isomer f,
1247; 10-hydroxylinalool, 1385; 8-hydroxylinalool, 1399. Retention
indices (for Chiraldex B-DM chiral column) were as follows: furanoid
linalool oxides, trans-(2R,5R), 1149; trans-(2S,5S), 1160; cis-(2R,5S),
1163; cis-(2S,5R), 1169; R-(-)-linalool, 1209; S-(+)-linalool, 1216;
pyranoid linalool oxides, trans-(2S,5R), 1271; trans-(2R,5S), 1284; cis-
(2S,5S), 1290; cis-(2R,5R), 1293. Response factors in relation to
1-octanol were as follows: cis- and trans-furanoid linalool oxide, 1.27;
cis- and trans-pyranoid linalool oxide, 1.32; (()-linalool, 1.19; 8-hy-
droxylinalool, 2.80.
Mass Spectra. trans-Furanoid linalool oxide m/z (relative intensity):
41 (34), 43 (71), 55 (38), 59 (100), 67 (24), 68 (25), 81 (12), 93 (21),
94 (27), 111 (13), 137 (3), 155 (2). cis-Furanoid linalool oxide m/z
(relative intensity): 41 (35), 43 (63), 55 (43), 59 (100), 67 (26), 68
(31), 81 (15), 93 (28), 94 (39), 111 (19), 137 (3), 155 (3). trans-Pyranoid
linalool oxide m/z (relative intensity): 41 (51), 43 (88), 53 (24), 55
(38), 57 (15), 59 (99), 67 (70), 68 (100), 79 (27), 94 (66), 137 (1), 155
(2). cis-Pyranoid linalool oxide m/z (relative intensity): 41 (34), 43 (64),
53 (16), 55 (24), 57 (10), 59 (89), 67 (54), 68 (100), 79 (20), 94 (53),
137 (2), 155 (3). Linalool m/z (relative intensity): 41 (97), 43 (100),
53 (15), 55 (64), 67 (20), 69 (38), 71 (89), 80 (31), 93 (55), 121 (12),
136 (5), 154 (<1, M+). Lilac aldehyde isomer a m/z (relative intensity):
41 (63), 43 (99), 55 (100), 67 (40), 69 (28), 71 (33), 81 (16), 91 (9),
93 (29), 111 (23), 125 (3), 153 (6). Lilac aldehyde isomer b m/z (relative
intensity): 41 (58), 43 (99), 55 (100), 67 (35), 69 (24) 71 (37), 81 (17),
91 (8), 93 (28), 111 (20), 125 (2), 153 (10). Lilac aldehyde isomer c
m/z (relative intensity): 41 (47), 43 (69), 55 (100), 67 (27), 69 (20), 71
(39), 81 (13), 91 (6), 93 (24), 111 (15), 125 (4), 153 (7). Lilac alcohol
isomer d m/z (relative intensity): 41 (58), 43 (100), 55 (90), 67 (40),
69 (23), 71 (28), 81 (15), 91 (11), 93 (56), 111 (69), 125 (5), 155 (6).
Lilac alcohol isomer e m/z (relative intensity): 41 (53), 43 (100), 55
(98), 67 (45), 69 (24), 71 (29), 81 (20), 91 (9), 93 (52), 111 (58), 125
(3), 155 (7). Lilac alcohol isomer f m/z (relative intensity): 41 (53), 43
(85), 55 (100), 67 (40), 69 (22), 71 (28), 81 (17), 91 (9), 93 (53), 111
(55), 125 (2), 155 (8). 10-Hydroxylinalool m/z (relative intensity): 41
(36), 43 (100), 53 (10), 55 (32), 67 (40), 68 (19), 71 (60), 79 (12), 81
(9), 93 (7), 137 (3), 152 (1). 8-Hydroxylinalool m/z (relative intensity):
41 (34), 43 (100), 53 (10), 55 (29), 67 (40), 68 (18), 71 (47), 79 (11),
81 (9), 93 (8), 137 (3), 152 (<1).
Sample Preparation. To determine the concentrations of linalool,
cis- and trans-furanoid linalool oxide, cis- and trans-pyranoid linalool
oxide, and 8-hydroxylinalool, 2 mL of liquid culture was filtered through
a 0.45 µm/25 mm nylon filter (Macherey-Nagel) and extracted with 2
mL of tert-butyl methyl ether (MTBE) prior to GC-MS. 1-Octanol was
used as internal standard for quantification. To determine the enantio-
meric distribution of linalool oxides, samples were analyzed via
enantioselective GC instead of GC-MS. All measurements were done
in triplicate.
Target Compound Identification. For the initial screening of 19
fungi, the occurrence of one fragment ion (m/z 153 for lilac aldehyde
or m/z 155 for lilac alcohol or m/z 111 for lilac aldehyde/alcohol) in a
time window of (0.5 min to the retention times of the chemically
synthesized standards was used as the criterion for transferring a strain
into the second, more detailed, screening run. For this second screening,
the target compounds, lilac aldehyde and lilac alcohol, were identified
by comparison with chemically synthesized standards on the basis of
their mass spectra and retention indexes. Selected ion monitoring (SIM)
using the following masses was applied: lilac aldehyde, m/z 153 (120×);
lilac alcohol, m/z 155 (120×); and lilac aldehyde/alcohol, m/z 111
(30×).
Figure 1. Linalool concentration-toxicity curve for B. cinerea 5901/2.
The next lowest concentration above the threshold concentration, above
which a sharp decrease in cell growth occurred, was chosen as maximum
precursor concentration, here 150 mg/L. The other strains showed
essentially the same toxicity profiles but varied concerning the maximum
concentration values, which are listed in Table 1.
initial linalool concentration of 200 mg/L. The pH of the MYB broth
was adjusted to pH 5 with HOAc. The concentration of the substrate
was analyzed every 2 days and finally after 9 days. To exclude de novo
biosynthesis of the target compounds, the selected strains were
cultivated under biotransformation conditions but without linalool.
RESULTS AND DISCUSSION
Initial Screening of Fungi, Batch Cultivation. Nineteen
fungal strains were screened for their capability to convert
linalool particularly into lilac aldehyde and lilac alcohol using
SPME-GC-MS as the monitoring technique. The strains were
grown as 15 mL liquid cultures in 40 mL SPME vials enabling
direct probing after 14 days of cultivation. The addition of 25%
(w/v) NaCl increased the analytical sensitivity by a factor of
10 due to the enhanced volatility of the target compounds (data
not shown). Potentially lilac aldehyde/alcohol-positive strains
were selected by searching time windows of (0.5 min around
the retention times of the reference substances for the occurrence
of at least one of the characteristic fragmentation ions m/z 155
(alcohol), m/z 153 (aldehyde), and m/z 111 (alcohol and
aldehyde). Due to the fact that only a relatively low concentra-
tion of the toxic precursor was chosen for this orienting
screening (30 mg/L), only low product concentrations near the
detection limit occurred, and the SPME-GC-MS analyses were
evaluated as indicative results: even those strains not giving
unambiguously positive results were chosen for a second
screening run under improved cultivation conditions. The seven
potentially positive strains were A. niger ATCC 16404, A. niger
DSM 821, B. cinerea 5901/2, B. cinerea 02/FBII/2.1, C.
cassiicola DSM 62475, S. cereVisiae Zymalor VL1, and S.
cereVisiae Uvaferm 228. To verify the preliminary results, we
aimed at developing optimized feed-batch cultivation in Erlen-
meyer flasks sequentially providing additional precursor and
glucose while avoiding toxic precursor concentrations. By this
means the final concentrations of linalool biotransformation
products were to raised, thus enabling us to identify not only
the major biotransformation products but also the lilac com-
pounds as metabolic byproduct.
Dry Biomass and Glucose Determination. The dry biomass was
determined gravimetrically using an infrared moisture analyzer (MA
100, Sartorius, Germany) by filtering 2 mL of homogenized liquid
culture through a dried, preweighed 0.45 µm/45 mm cellulose acetate
membrane filter (Schleicher & Schuell, Germany). The concentration
of glucose was determined enzymatically (YSI 2700 Biochemistry
Analyzer, Yellow Springs Instruments, Yellow Springs, OH).
Chemical and Biological Control Experiments. The chemical
stability of the substrate (()-linalool was verified under cultivation
conditions during a period of 9 days without inoculum and with an
Linalool Toxicity. Strain-specific linalool concentration-
toxicity profiles were determined by measuring the final cell
dry weight after incubation of the fungi for 4 days in the
presence of increasing concentrations of linalool. Figure 1
exemplarily illustrates the toxic effects of linalool on B. cinerea
5901/2. Due to an observed sharp decrease in viability at a