Hydrocarbons are the most used biomarkers for petroleum exploration and paleoenvironment analyses. Ketones and esters can also provide adequate information. The most representative examples are alkenones, which are used as paleoceanographic proxies [1] , and fatty acids that serve as biomarkers of microalgae and bacteria [2] . Despite their similarities with ketones and esters, aldehydes are not employed as effective proxy biomarkers.

Few studies have reported the presence of long-chain aldehydes compared to other compounds in sediment surface samples. Previously, gas chromatography/ mass spectrometry (GC/MS) analyses of a stream deposit affected by industrial production activities revealed the presence of an aldehyde, possibly generated by the bacterial resolution of a high-carbon-number normal unsaturated compound [3] . Aldehydes with a high CPI (Carbon Preference Index) value have been detected from the surface sediment of the Unagi-ike pond, possibly indicative of an aldehyde from a high-vegetable land source [4] . Aldehydes reportedly detected from the sediment of the Spanish Cadiz Bay are classified into three patterns, i.e., 1) aldehydes originating from a land source corresponding to peaks of C₂₈-C₂₉, 2) aldehydes originating from an alga or a microorganism corresponding to peaks of C₁₇-C₁₉, and 3) mixture of the above two sources, respectively. The aldehyde distribution revealed the reduction environment of the surface sediment [5] . The abovementioned studies have not reported detailed MS analyses of the detected natural aldehydes.

In this study, the GC/MS analysis of long-chain aldehydes extracted from recently extracted coral is reported using standard conditions, i.e., no special equipment or methodology was used. The results obtained with this method helped to identify aldehydes in sediment samples. Based on this report, a new proxy, i.e., an aldehyde, can be used as a biomarker.

The analyzed coral sample was sampled by boring in the Malindi Marine National Park, located on the eastern coast of Kenya. The sample was collected 15 km southwest from the mouth of the Sabaki River in 2003. The coral core sample was dried at room temperature, and the coral core surface was scraped off to approximately 5 mm in thickness using a grinder to prevent contamination before powdering.

Traditional Soxhlet extraction using dichloromethane/methanol (93/7, v/v) was performed for 70 h to extract the biomarker. The extracted solvent was concentrated using a rotary evaporator. The isolated lipid was divided into four fractions using silica-gel column chromatography. A hydrocarbon fraction was obtained using two column volumes of n-hexane; a polyaromatic hydrocarbon fraction was obtained with two volumes of n-hexane/dichloromethane (2/1, v/v); an aliphatic ketone/ester fraction was obtained with seven volumes of n-hex- ane/dichloromethane (1/1, v/v); and a polar fraction was obtained with excess dichloromethane/methanol (1/1, v/v). Then, three fractions were examined via GC/MS: one corresponding to hydrocarbons, another to polyaromatics, and the other to aliphatic ketone/ester. A Shimadzu QP-2010 plus GC-MS system equipped with a 30-m fused silica capillary column (Thermo Scientific TG-5MS, 0.25 mm i.d., 0.25 μm film thickness) and a splitless column injector was used. The following temperature program was utilized: isothermal conditions at 60˚C for 1 min; 60˚C - 175˚C at 10˚C /min; 175˚C - 225˚C at 6˚C/min; 225˚C - 300˚C at 4˚C/min; and isothermal conditions at 300˚C for 20 min. MS data were recorded in the electron impact mode at 70 eV scanning from m/z 50 to m/z 520. This methodology corresponds to the typical analysis for biomarkers.

The analysis of the hydrocarbon and polyaromatic fractions of this study did not provide any useful information. However, in the aliphatic ketone/ester fraction, aldehydes were successfully detected. Figure 1 shows the analysis result (total ion chromatogram, TIC) for the ketone/ester fraction. A long-chain aldehyde (C₁₉-C₂₇) did not predominantly exhibit an even number of carbons with C₂₂ corresponding to the highest fraction. In contrast, C₂₈-C₃₀ aldehydes were dominant in the C₂₇-C₃₀ area. In addition, long-chain ketones such as C₂₉, C₃₁, C₃₃, and C₃₅ (keto-2-one, represented as ⊗-) were detected. Long-chain ketones with even-numbered carbons were not detected. The retention index of aldehydes was calculated based on the retention time of both fatty-acid methyl esters in the ketone/ester fraction and the n-alkanes in the hydrocarbon fraction. Table 1 summarizes the retention indexes and characteristic cleavage ions from long-chain aldehydes. The standardization based on the fatty-acid methyl esters is not general; it was rather performed to show the procedure to determine the retention time of aldehydes. Notably, the retention times of the long-chain aldehydes and fatty-acid methyl esters slightly overlapped. The peak corresponding to long-chain aldehydes was buried under the peak corresponding to the fatty- acid methyl ester, and the resultant long-chain aldehyde was not detected from the analyses, where the content of the long-chain aldehyde is relatively less than that of the fatty acid methyl ester. Hence, few studies have reported the analysis of long-chain aldehydes.

The mass spectra of C₂₆ and C₂₈ long-chain aldehydes were recorded from C₂₀ in Figure 2. The mass spectral feature of long-chain aldehydes was the presence

*Retention Index was calculated based on the retention time of FAME (fatty acid methyl ester) and n-alkane.

of a dominant base peak at m/z 82. A second or third peak was observed at m/z 57 or 96, followed by a peak at m/z 110 and even-numbered ions of m/z 124 or 138. The M-18 ion, which was formed by the loss of H₂O, and M-46 or M-84 were characteristic for long-chain aldehydes of the number of all carbon. Even-numbered ions of continuation m/z 82 and 96 or 110 or 124 exhibited 68 + 14n, corresponding to ions that are absent in the other compounds and are characteristic for long-chain aldehydes. A molecular ion (M⁺) was not detected, and m/z 71 < m/z 68 was characteristic of long-chain aldehydes by which number of carbon is less than 22.

The peak corresponding to m/z 82 corresponded to cyclohexene formed by the McLafferty rearrangement; in addition, the peaks corresponding to m/z 96, 110, and 124 corresponded to a C-6 ring structure [6] .

The long-chain aldehydes detected from coral collected from the east coast of Kenya are analyzed by gas chromatography mass spectrometry (GC/MS) using the typical procedure for biomarker analysis. The detection of long-chain aldehydes needs to consider the overlap in the retention time with the fattyacid methyl ester. After assessing the difference in the retention time between aldehydes and fatty acids methyl ester, aldehydes were easily detected using the typical analytical procedure for biomarkers analysis. The following characteristics of the mass spectral peaks were confirmed by the GC/MS analysis of the long-chain aldehyde isolated from coral reefs. (1) An even-numbered molecular weight ion, corresponding to m/z 68 + 14n, where m/z 82 is the base peak; (2) M-18 by the loss of water; (3) A long-chain aldehyde was confirmed by (1); the number of carbons in aldehyde can be detected by (2) and the retention index despite the presence of a molecular ion (M⁺).

Based on the results of this study, it is feasible to establish aldehydes as a new environmental proxy that can be useful when these types of compounds are found in surface samples.

The author wishes to express his gratitude to Professor H. Kayanne and his lab member Dr. N. Nakamura for supplying the coral sample.

Ogihara, S. (2018) GC/MS Analysis of Long-Chain Aldehydes from Recent Coral. American Journal of Ana- lytical Chemistry, 9, 46-51. https://doi.org/10.4236/ajac.2018.91004