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Reply

Response to Comment by Bence et al.

Frances D. Hostettler *, Robert J. Rosenbauer, Keith A. Kvenvolden

US Geological Survey, 345 Middle®eld Road, MS409, Menlo Park, CA 94025, USA

Received 25 February 2000; accepted 8 May 2000 (returned to author for revision 12 April 2000)

We welcome the opportunity to respond to the Com-ment of Bence et al. (2000) regarding the suitability of the new geochemical parameter we have introduced. Part of their comment, however, addresses issues either not directly related to our paper, or issues published else-where. The lengthy comment seems a disproportionate reaction to what was a paper of limited scope, simply introducingonenew geochemical parameter, the refrac-tory index (RI). The RI is a ratio of triaromatic steranes (T) to methyl chrysenes (C) (T/C); these compounds are ubiquitous in petroleum and are two of the most refractory components of the suite of polycyclic aro-matic hydrocarbons (PAH) found in petroleum. The RI, therefore, was proposed as a source parameter poten-tially useful, in concert with other relevant geochemical parameters, in the correlation of oils over a wide range of environmental weathering conditions.

The following paragraphs address some of the issues raised by Bence et al. (2000).

1. Sampling

With respect to what Bence et al. (2000) refer to as ``Inadequate Sampling'', we acknowledge that we had a limited sample set. The key question, however, is whe-ther it is adequate to address the issues raised in our paper. Our work focused on three known oils from the Prince William Sound (PWS) area: North Slope crude oil from theExxon Valdezoil spill, California/Monterey oil spilled during the 1964 Great Alaskan Earthquake

(Kvenvolden et al., 1995), and Katalla seep oil, an onshore oil from the Gulf of Alaska (GOA). The main point of our paper was to apply the refractory index to these oils and determine whether it could reliably dis-criminate among them at di€erent weathering stages, which it did. We also analyzed a few coal samples from the region, including coal distributed in strands all along the intertidal beach at Katalla, to see if they contained the same compounds used in the RI. In general, the coals gave very low or zero RI values, due to the absence, or extremely low amounts, of triaromatic steranes. In addi-tion, we examined benthic sediments from the study area to see if the RI could help evaluate whether any of the above oils contribute to the hydrocarbon back-ground therein. These benthic sediments also gave very low to zero RI values, at least an order of magnitude lower than any of the above oils, but comparable to the RI range of the coal samples.

Bence et al. (2000) fault our work for not examining other GOA oils in addition to Katalla, such as seep oil from Yakataga, located further east along the shore of the GOA, and Tertiary shales. Our choice of Katalla seep oil was a direct response to the large body of work in which Katalla oil is emphasized (Bence et al., 1996; Douglas et al., 1996; Boehm et al., 1997, 1998; Page et al., 1996), and hydrocarbon distributions for the Katalla seep oil are characterized as ``...representative of other

Gulf of Alaska seep sources'' (Page et al., 1996). It is only recently, after our above work was completed, that Page et al. (1998) abandoned Katalla seep oil and abruptly shifted emphasis to Yakataga seep oil. The focus on the Tertiary shales mentioned by Bence et al. (2000) is even more recent. Work from as late as 1998 and 1999 (Boehm et al., 1998; Page et al., 1999) still referred to a PWS/GOA ``seep-derived background of PAH'', with no mention of the Tertiary shales. When our work was

0146-6380/00/$ - see front matter Published by Elsevier Science Ltd. P I I : S 0 1 4 6 - 6 3 8 0 ( 0 0 ) 0 0 0 6 3 - 2

www.elsevier.nl/locate/orggeochem

* Corresponding author. Tel.: 329-4584; fax: +1-650-329-5590.

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done (completed for oral presentation at the National American Chemical Society meeting, March, 1998), it was following the lead of the above-cited studies.

In fact, however, we had examined a sample of Yaka-taga seep oil, Johnston Creek oil, and had two primary reasons to exclude it from the above work. First, Yaka-taga is signi®cantly further east of PWS in the GOA than Katalla. Even the published aerial photographs in Page et al. (1995) of the turbidity and suspended sediment plumes carried by the Alaskan Current from the Yaka-taga area toward PWS show that Kayak Island, Okalee Spit, and Cape Suckling disrupt the ¯ow towards PWS, leaving a partial disconnect which appears to hinder sediment transport.

Second, we examined the aliphatic biomarker and the PAH pro®les of the Johnston creek oil. We did ®nd that its RI is low, similar to those of the coals and the benthic sediments, as stated in the Comment by Bence et al. However, even with a low RI, triaromatic steranes were present. These, and the regular steranes, had a somewhat uncommon distribution. The sterane pro®le (SIM ofm/z217, Fig. 1B) shows a strong dominance of C29steranes, which may indicate that terrestrial higher

plants were the dominant precursors of the organic matter in the oil (Lu and Kaplan, 1992; Clayton, 1993). Because C29 steranes give rise to C28-triaromatic

ster-anes, this distribution carries over to the triaromatic sterane pro®le (extracted ion pro®le m/z 231, Fig. 1B). This pro®le shows a less common distribution pattern of dominance by the C28-triaromatic sterane epimers, as

compared to the very common and more typical distribu-tion found in most oils (see discussion of triaromatic steroids (steranes) in Volkman et al., 1997). A typical pattern, such as that seen inExxon Valdezoil (EVO), is shown in Fig. 1A. The distributions of regular and triaromatic steranes in the Johnston creek oil, coupled with low biomarker levels in general, probably indicate that this oil was originally sourced from coal. The important point, however, is that this distinctive pattern of regular steranes and triaromatic steranes is not evi-dent in the biomarker or PAH pro®les of any of the o€shore GOA or PWS sediments that we have exam-ined (Fig. 1E and F). This is the primary reason why we did not include Johnston creek oil in our discussion of RI.

Additionally, since the completion of our earlier work, we have examined several other Yakataga seep oils. We have found that oil from Mundy creek, Smokey creek, another sample from Johnston creek, and even Samovar Hills oil, all share this particular sterane and triaromatic sterane distribution (Fig. 1C and D), mak-ing them all questionable sources for the hydrocarbon background in the benthic sediments.

We would, however, very much like to examine the newly suggested Tertiary shales in future work. The shales, in particular, seem plausible in that their PAH are

probably suciently adsorbed within the shale matrix so as to make them non-bioavailable and resistant to weathering. These two factors were the primary reasons for the Short et al. (1999) challenge to the claim that ``seep-derived PAH'' were the source of the PAH back-ground in PWS, since seep-derived PAH would be both bioavailable and subject to weathering, and no sub-stantive evidence of oil-sediment associations obviating these processes has yet been provided.

2. Katalla coal

The next issue raised by Bence et al. (2000) regards our identi®cation of the ``coaly'' material which was collected from the surface of Katalla beach in 1997 (latitude 60 11.20 N and longitude 144 31.20 W). Examination of the grain morphology of the sample under a binocular microscope showed features char-acteristic of coal Ð black color, semi-metallic lustre, blocky shape, and conchoidal fractures (Dell and Booth, 1977). These characteristics, coupled with the high bulk carbon content of the sample (80% by weight), clearly identi®es the Katalla beach sample as nearly pure coal. In addition, a second sampling trip two years later (4/99; latitude 6008.30N and longitude 14427.20 W) has provided new material which is similar in appearance and yields comparable Total Organic Car-bon (TOC) values: 82 and 74% by weight (J. Kolak, personal communication). These analyses contrast mark-edly with Bence et al.'s highest value for Katalla beach sediment of 11.62% TOC. While beaches are highly dynamic environments, the fact that our two distinct samples yield nearly identical results may indicate that Bence et al. (2000) were not successful in obtaining a representative sample of the material constituting the strand lines on Katalla beach. We found abundant material on the beach, and were easily able to collect black material from thick (>5 mm) accumulations. Whereas our sampling collected only the coal material, theirs may have included extraneous inorganic beach material.

Conventional aliphatic biomarker ratios for the 1997 Katalla coal sample given in Carlson et al. (1997) show this sample to have parameters indicating immaturity. However, new vitrinite re¯ectance data on the 1997 and 1999 Katalla beach samples indicate high maturity, that is, 2.47 and 2.53% Ro, with indication of possible

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Fig. 1. C27±C29sterane (SIM,m/z217) and C26±C28triaromatic sterane (extracted ion pro®le,m/z231) distributions in: (A) a typical

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broad convergence of hydrocarbon parameters to values characteristic of these sediments.

3. Mass balance

Another problem noted by Bence et al. (2000) was the issue of ``Mass Balance Constraints''. Consideration of TOC and total PAH (TPAH) was outside the scope of our paper, and the comment really is directed at work pub-lished in Short et al. (1999). However, in response to the concern of Bence et al. (2000), we will mention some of our current work that resolves the inconsistency with TOC, TPAH, and carbon mass-balance in GOA sediments. New analysis of TPAH in coal particles isolated directly from GOA sediments (near Kayak Island) via density separation (J. Kolak, personal communication) gives a concentration of TPAH exceeding 400mg/g coal (Short et al., 2000). Work in progress in conjunction with these separations shows that there is a large particle-size/sur-face-area e€ect on the eciency of PAH extraction from coal. TPAH analyses on source coal particles of a grain size similar to the coal particles isolated from GOA sedi-ment yield comparable TPAH concentrations (300mg/ g coal). Both these measurements, therefore, give sig-ni®cantly greater concentrations of TPAH in coal than we had previously reported and, together, are of a mag-nitude that obviates Bence et al.'s mass balance concerns.

4. Thermal maturity

Bence et al. (2000) attempt to limit the applicability of the RI by raising thermal maturity considerations having to do with the thermal stability of long chain vs. short chain triaromatic steranes. However, thermal maturity is not the relevant issue in this context. The three oils and the coals under consideration for the RI parameter are petrogenic substances which are separated from their respective source reservoirs. This means that they carry their molecular signatures into the environment; thermal maturity is already incorporated into that sig-nature. In the environment the relevant issue is suscept-ibility to weathering. The two terms in the RI, the triaromatic steranes and the methyl chrysenes, have been shown in other studies (e.g. Killops and Howell, 1988; Munoz et al., 1997) and acknowledged within Bence et al. (1996) and the Current comment, to be highly resistant to weathering.

Furthermore, we note an apparent double standard in the Bence et al. Comment, in that the index used throughout the entire body of their work as the primary discriminant to di€erentiate PWS oils, the DPI or C2-Dibenzothiophene/C2-Phenanthrene Index, has been rigorously evaluated for its source and weathering characteristics (Douglas et al., 1996), but not for

ther-mal maturity. The reason is that, as with the RI, therther-mal maturity is not the relevant issue in this context.

5. Other molecular indicators

We strongly agree that a single parameter, like the RI, is insucient to make a case for source correlation. We state in the publication that the parameter ``supports'' other data. It was never intended to stand alone. Some-times, even with an apparently compelling correlation, conclusions can be in error or may not consider all the alternatives. For example, although the body of work sup-porting the Bence et al. Comment used the DPI extensively to evaluate oils and the natural petrogenic background in PWS/GOA benthic sediments, the possibility of a coal contribution was dismissed (Page et al., 1996). Yet Short et al. (1999) showed that the DPI for Katalla seep-oil and Katalla beach coal, for example, are essentially identical, and that the DPI value is also in the same range as those of the benthic sediments. Also, the bio-marker oleanane was put forth as ``a speci®c indicator for seep-derived petrogenic background'' (Page et al., 1997) and coals were discounted, without analysis, as unlikely sources of substantial amounts of oleanane (Bence et al., 1996). But Short et al. (1999) demon-strated that the oleanane index has a comparable value in GOA coals as well as in Katalla oil. There is not ade-quate justi®cation for dismissal of coal as a potential source of PAH Ð we now have preliminary data on benthic sediment from near Kayak Island in the GOA which show coal to contribute at least 20% of the total PAH. Bence et al. in their Comment ®nally acknowledge the presence of coal in the benthic sediments, although they claim the coal is in low abundance and too mature to contribute signi®cant amounts of PAH to the back-ground. The coal in the Kayak Island benthic sediment provides some evidence to the contrary, and additional work in progress will further address this claim.

6. Conclusion

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the parameter provides information but is not useful as a discriminant among them. In all cases, additional correlating factors must be used.

There are other issues raised in the comment by Bence et al., but again, they are beyond the scope of our ori-ginal paper and are best addressed in a separate pub-lication. This is an evolving study of a very complex system and there is still more to be learned.

Associate EditorÐJ. Curiale

References

Bence, A.E., Kvenvolden, K.A., Kennicutt II, M.C., 1996. Organic geochemistry applied to environmental assessments of Prince William Sound, Alaska, after the Exxon Valdez oil spill Ð a review. Organic Geochemistry 24, 7±42.

Bence, A.E., Burns, W.A., Mankiewicz, P.J., Page, D.S., Boehm, P.D., 2000. Comment, this issue.

Boehm, P.D., Douglas, G.S., Burns, W.A., Mankiewicz, P.J., Page, D.S., Bence, A.E., 1997. Application of petroleum hydro-carbon chemical ®ngerprinting and allocation techniques after the Exxon Valdez oil spill. Marine Pollution Bulletin 34, 599± 613.

Boehm, P.D., Page, D.S., Gil®llan, E.S., Bence, A.E., Burns, W.A., Mankiewicz, P.J., 1998. Study of the fates and e€ects of the Exxon Valdez oil spill on benthic sediments in two bays in Prince William Sound, Alaska. 1. Study design, chemistry, and source ®ngerprinting. Environmental Science and Technology 32, 567±576.

Carlson, P.R., Kvenvolden, K.A., Hostettler, F.D., Rosen-bauer, R.J., Warden, A., 1997. Fate of spilled oil in Prince William Sound: diary of a forensic geology study. US Geol-ogical Survey Open-File Report 97±518. 88 pp.

Clayton, J.L., 1993. Composition of crude oils generated from coals and coaly organic matter in shales. In: Law, B.E., Rice, D.D. (Eds.), Hydrocarbons from Coal. AAPG Studies in Geology No. 38, pp. 185±201.

Dell, C.I., Booth, W.G., 1977. Anthropogenic particles in the sediments of Lake Erie. Journal of Great Lakes Research 3, 204±210.

Douglas, G.S., Bence, A.E., Prince, R.C., McMillan, S.J., But-ler, E.L., 1996. Environmental stability of selected petroleum hydrocarbon source and weathering ratios. Environmental Science and Technology 30, 2332±2339.

Killops, S.D., Howell, V.J., 1988. Sources and distribution of hydrocarbons in Bridgewater Bay (Severn Estuary, UK) intertidal surface sediments. Estuarine, Coastal and Shelf Science 27, 237±261.

Kvenvolden, K.A., Hostettler, F.D., Carlson, P.R., Rapp, J.B., Threlkeld, C.N., Warden, A., 1995. Ubiquitous tarballs with a California-source signature on the shorelines of Prince William Sound, Alaska. Environmental Science and Tech-nology 29, 2684±2694.

Lu, S.-T., Kaplan, I.R., 1992. Diterpanes, triperpanes, and aromatic hydrocarbons in natural bitumens and pyrolysates from di€erent humic coals. Geochimica et Cosmochimica Acta 56, 2761±2788.

Munoz, D., Guiliano, M., Doumenq, P., Jacquot, F., Scherrer, P., Mille, G., 1997. Long term evolution of petroleum bio-markers in mangrove soil (Guadeloupe). Marine Pollution Bulletin 34, 868±874.

Page, D. S., Boehm, P. D., Douglas, G. S., Bence, A. E., 1995. Identi®cation of hydrocarbon sources in the benthic sedi-ments of Prince William Sound and the Gulf of Alaska fol-lowing the Exxon Valdez oil spill. In Wells, P.G., Bulter, J.N., Hughes, J.S., (Eds.)Exxon ValdezOil Spill: Fate and E€ects in Alaskan Waters, ASTM, STP 1219, pp. 41±83. Page, D.S., Boehm, P.D., Douglas, G.S., Bence, A.E., Burns,

W.A., Mankiewicz, P.J., 1996. The natural petroleum back-ground in subtidal sediments of Prince William Sound, Alaska. Environmental Toxicology and Chemistry 15, 1266± 1281.

Page, D.S., Boehm, P.D., Douglas, G.S., Bence, A.E., Burns, W.A., Mankiewicz, P.J., 1997. An estimate of the annual input of natural petroleum hydrocarbons to sea¯oor sedi-ments in Prince William Sound, Alaska. Marine Pollution Bulletin 34, 744±749.

Page, D.S., Boehm, P.D., Douglas, G.S., Bence, A.E., Burns, W.A., Mankiewicz, P.J., 1998. Reply to Letter to the Editor. Environmental Toxicology and Chemistry 17, 1651±1652. Page, D.S., Boehm, P.D., Douglas, G.S., Bence, A.E., Burns,

W.A., Mankiewicz, P.J., 1999. Pyrogenic polycyclic aromatic hydrocarbons in sediments record past human activity: A case study in Prince William Sound, Alaska. Marine Pollu-tion Bulletin 38, 247±260.

Short, J.W., Kvenvolden, K.A., Carlson, P.R., Hostettler, F.D., Rosenbauer, R.J., Wright, B.A., 1999. Natural hydro-carbon background in benthic sediments of Prince William Sound, Alaska: oil vs. coal. Environmental Science and Technology 33, 34±42.

Short, J.W., Kvenvolden, K.A., Carlson, P.R., Hostettler, F.D., Rosenbauer, R.J. Wright, B.A., 2000. Reply to Letter to the Editor. Environmental Science and Technology 34, 2066±2067.

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