Chemical Geology 175 Ž2001. 319–341 www.elsevier.comrlocaterchemgeo Causes of colour and fluorescence in speleothems Philip van Beynen a,) , Rick Bourbonniere b, Derek Ford a , Henry Schwarcz a a b School of Geography and Geology, McMaster UniÕersity, Hamilton, Ontario, Canada L8S 4K1 National Water Research Institute, EnÕironment Canada, Burlington, Ontario, Canada L7R 4A6 Received 8 June 1999; accepted 26 May 2000 Abstract Speleothems fluoresce, when illuminated with UV light, between 410 and 460 nm. In this study, we attempted to determine the nature of the fluorophores, thought to be either trace elements or organic matter trapped in the calcite. Fluorescence of solid speleothems and organic species extracted from the calcite were measured to quantify their contribution to the observed fluorescence of the speleothems. All speleothems and extracts gave similar spectra with broad emission maxima centred around 410–430 nm, and two excitation maxima at approximately 255 and 330 nm. The organic compounds were partly characterized using fulvic acid ŽFA. –humic acid ŽHA. separation and molecular size fractionation. Trace elements, determined by neutron activation analysis, do not appear to be responsible for the observed spectra. Organic matter, particularly FAs, were found to be the dominant fluorophore in the calcite. Of the FA, the dominant fractions were the hydrophilics. Darker speleothems, although having higher concentrations of FA and HA than light speleothems, had lower emission intensities, due to self-absorption. Average particulate organic matter ŽPOM., FA, HA, and total organic matter ŽTOM. concentrations for the dark speleothems were twice that of their light counterparts. q 2001 Elsevier Science B.V. All rights reserved. Keywords: Caves; Fluorescence; Fulvic acids; Humic acids; Speleothems 1. Introduction Speleothem is a generic term given to stalagmites, stalactites, and flowstones consisting of calcite or other mineral cave deposits. They display two important types of optical properties. To begin, when viewed either in reflected or transmitted visible light, ) Corresponding author. Fax: q1-905-546-0463. E-mail addresses: [email protected] ŽP. van Beynen., [email protected] ŽR. Bourbonniere., [email protected] ŽD. Ford., [email protected] ŽH. Schwarcz.. speleothems display varying degrees of colour hue and intensity. Secondly, when illuminated by ultraviolet light, they emit fluorescent light in the visible range. Both of these effects are presumably connected to the presence of minor constituents in these calcitic deposits since chemically pure calcite is neither coloured nor fluorescent. Some of these properties have been attributed to the presence of trace elements in the calcite, but since the early work of Gilson and MacCarthney Ž1954., it has been suggested that this fluorescence is caused by organic substances, a supposition supported by Gascoyne Ž1977., Lauritzen et al. Ž1986., and White and Brennan Ž1989.. Lauritzen et al. Ž1986. in particular 0009-2541r01r$ - see front matter q 2001 Elsevier Science B.V. All rights reserved. PII: S 0 0 0 9 - 2 5 4 1 Ž 0 0 . 0 0 3 4 3 - 0 320 P. Õan Beynen et al.r Chemical Geology 175 (2001) 319–341 demonstrated that much of the colour must be due to the presence of organic substances Žhumic compounds. dispersed in the calcite. Similarly, Shopov et al. Ž1994. argued that the fluorescent properties of speleothems were the result of the presence of organic compounds trapped in speleothems. Ramseyer et al. Ž1997. found that low molecular weight fulvic acids ŽFAs. were the dominant constituent of organic matter derived from speleothems, a result confirmed by White Ž1997.. Finally, Baker et al. Ž1998. showed a strong relationship between the luminescence properties of speleothems and the extent of soil humification and rainfall above a cave. Calcitic cave deposits contain paleotemperature records as derived from oxygen isotopes ŽSchwarcz, 1986; Gascoyne, 1992. and paleovegetation records as seen in the carbon isotope records ŽDorale et al., 1992.. These records can be dated with U-series analysis to a precision of ; 1% up to 350 ka ŽLi et al., 1989.. Broecker et al. Ž1960. using 14 C dates found laminae in parts of speleothems that were annual in resolution. Such laminae are differentiated through changing colour of the calcite and are composed of a couplet of light and dark calcite. Their presence has also been revealed using fluorescence microscopy ŽBaker et al., 1993; Genty and Quinif, 1996; Shopov et al., 1989, 1994.. Production of annual laminae within calcite is to be expected: organic matter in litter and soil decomposes due to activity of microorganisms and percolation waters then transport the products through the soil and rock to the cave. Throughout the passage, organic matter may be altered by further decomposition or removed by the filtration processes occurring in the mineral medium and rock. However, some organic matter remains in the solution. A complicating factor is that some ancient organic substances may also be obtained from the dissolution of the limestone bedrock. Upon reaching the cave, degassing of CO 2 from aqueous solution may lead to calcium carbonate saturation and calcite or aragonite precipitation. Calcite has been shown to be an efficient absorber of organic matter, especially of lipid material and amino acid substances ŽSuess, 1970; Carter, 1978.. Mitterer Ž1968. found that organic matter may even induce CaCO 3 precipitation by concentrating calcium ions. The principal subjects of this paper are the precise sources of the fluorescence in speleothems and the relationships between fluorescence and colour hue and density. These should explain the major chemical differences between light and dark calcite. To explain the source of fluorescence in speleothems, it must be recognized that organic substances are not the only natural entities, which might fluoresce in speleothems. Trace and rare earth elements such as samarium, dysprosium, europium, terbium and manganese have been shown to produce fluorescence when coprecipitated with calcite; in particular, europium and dysprosium fluoresce at the same wavelengths as the organic acids ŽMason and Mariano, 1990.. The calcium ion can be replaced in the lattice by these smaller divalent and trivalent fluorescing cations through substitution ŽTerakado and Masuda, 1988.. Organic substances in soil pore waters may be divided into three components that are operationally defined by their solubility in acid–base ŽClapp and Hayes, 1999.. FAs are soluble in all conditions of acid–base; humic acids ŽHAs. precipitate when the solution becomes acidic Žas pH approaches 2.; humin is insoluble in any solution, although it may be mechanically flushed from soils. The residence times of these compounds in soils may range from decades to hundreds of years for FAs and thousands of years for HAs ŽSchlesinger, 1977.. The molecular weights of FAs tend to be smaller than HAs ŽSuffett and MacCarthy, 1987.. Further differentiation of the FAs is possible by partitioning them into hydrophilic acids ŽHPIA. and hydrophobic acids ŽHPOA., bases, and neutrals ŽLeenheer, 1985.. The structural complexity of FAs has hindered their further characterization ŽErtel, 1988.; however, major functional groups identified thus far include carboxyls, phenolic hydroxyls, and alcohols ŽVisser, 1983.. NMR studies have revealed ketoneraldehyde, carboxyl, aliphatic and aromatic hydroxyl groups. Spectroscopic studies by Wilson et al. Ž1988. confirmed these findings. The typical molecular weight of FAs is 800–1000 Da. HAs are found to range greatly, from 2000 to 300,000 Da ŽSuffet and MacCarthy, 1987.. Their differentiation can be undertaken by gel permeation chromatography or ultrafiltration ŽWershaw and Aiken, 1985.. Much work has been done on the fluorescence of these substances ŽMiano et al., 1988; Senesi, 1990; Senesi et al., 1991; Simpson et al., 1997a.. FA wavelengths of fluorescence emission P. Õan Beynen et al.r Chemical Geology 175 (2001) 319–341 321 are usually microscopic in scale. To investigate their differences, larger samples that exhibit more uniform colour are required. We selected a set of 12 speleothems from a collection at McMaster University, ranging in colour from translucent white to opaque to nearly black. Their fluorescence was measured in the solid calcite and in solution. Solutions were fractionated into the FAs, HAs, and particulate organic matter ŽPOM.. The hydrophilic and hydrophobic components of FAs were then separated for measurement of their individual fluorescence and dissolved organic carbon ŽDOC.. Sub-samples of the solid calcite were subjected to neutron activation analysis to determine whether there could be any significant trace element or rare earth element contributions to the fluorescence spectra. These procedures are summarised in a flowchart, Fig. 1. Fig. 1. Flowchart of analysis undertaken on speleothems: ŽA. dissolved speleothems, and ŽB. solid speleothems. 3. Provenance of the sample speleothems maxima and excitation peaks vary between 410–520 and 320–470 nm, respectively, depending on their environment ŽSenesi, 1990; Senesi et al., 1991.. HAs have longer excitation and emission wavelengths, with respective peak intensities at 480 and 540 nm ŽHayase and Tsubota, 1985.. 2. Research design and procedures Where alternating light and dark calcite bands, denoting annual laminae, occur in speleothems they In addition to colour hue and density, an important criterion for selecting the speleothems was the current variety of climate and natural vegetation found at the site of collection. A considerable natural range was obtained. The samples were selected from the following locations. Crowsnest Pass Ž49830X N, 114830X W. and Bow Valley ŽRatsnest Cave, 51845X N, 115830X W. in the Rocky Mountains of Alberta, British Columbia. The settings range from boreal forest to alpine shrub tundra. Winters are cold and there is a strong spring Table 1 Present climate conditions at sampling locations Site Mean annual temperature Ž8C. Mean daily Jan. temperature Ž8C. Mean daily July temperature Ž8C. Mean total precipitation Žmm. Mean cave temperature Ž8C. Crowsnest Pass Cold Water Ratsnest Jewel McFail’s Kimberley Cayman Brac OFD 3 8.5 8.4 6.6 7.5 24.1 25.5 8.3 y10 y7.5 y6.5 y4.8 y4.7 30.4 22.5 2.5 15 23 22.3 18.1 19.1 17.8 28.5 14 1000 820 263 525 960.4 284 1025 2200 1.8 8.5 8.4 9.4 7.5 24.1 25.5 8.3 P. Õan Beynen et al.r Chemical Geology 175 (2001) 319–341 322 thaw. Samples — CNP, CNPLB, and CNPDB Žlight and dark layers from the same speleothem., RNCP and RNCF2. Jewel CaÕe, Black Hills, South Dakota Ž43844X N, 103855X W.. The setting is sub-humid today, at the lower limit of ponderosa forest. There is a wellmarked spring thaw. Sample — JC11. Cold Water CaÕe, Iowa Ž4283X N, 90839X W. is beneath a deciduous forest but close to the tall grass–prairie transition. There is a spring thaw. Sample — CW4. McFail’s CaÕe, New York Ž38822X N, 86820X W. is located in the Carolinian forest zone with milder winters than the previous sites but with spring and earlier snap thaw events. Samples — MF1 and MF2. Ogof Ffynon Ddu, Wales Ž528N, 3830X E. is in a temperate maritime setting beneath a deciduous Žash, oak. forest. Sample — OFD. Rebecca’s CaÕe, Cayman Brac Ž19844X N, 79848X W. has a tropical maritime climate with a summer rainfall bias. There is scrub vegetation on phytokarst above the cave. Sample — RCB. Kimberley Ranges, Western Australia Ž268S, 1208E. represents the warm arid limits for speleothem deposition today, with desert–savannah vegetation and sparse summer rains. Sample — WAH. Further details of the locations and colours of the sample speleothems are given in Tables 1 and 2. The speleothems mentioned in Table 2 are arranged according to colour gradation, lightest to darkest. Six Table 2 Colour of the solid speleothems Sample Light WAH MF1 CNPLB RNCF2 CW4 RNCP Dark MF2 OFD JC11 RCB CNPDB CNP Colour Description ŽMunsell Soil Chart. N 8r0 5Y 7r1 10YR 7r1 5Y 8r1 5Y 8r2.5 5Y 8r2.5 10YR 6r1 5YR 4r8 5YR 5r3 5R 4r4 7.5R 3r2 7.5R 1.7r1 Grayish white Light gray Light gray Light gray Light gray_pale Yellow Light gray_pale yellow Brownish gray Reddish gray Dull reddish brown Dull reddish brown Dark reddish brown Reddish black light and six dark coloured speleothems were selected. 4. Analytical methods 4.1. Isolation of humic substances The traditional definitions of soil humic substances are based simply on their acid and base solubility. Thus, soil organic matter, which is insoluble in both acid and base, is called humin. HAs are soluble in base but insoluble in acid, while FAs are soluble in both acid and base ŽStevenson, 1985; Swift, 1985.. Decalcification Žwith HCl. is commonly carried out on soil samples prior to base extraction of humic substances using a variety of alkaline extractants ŽStevenson, 1982.. The definition for separating HAs from the base extract is usually pH s 1, but pH 1.5 and 2 have been used ŽSwift, 1985; Richmond and Bourbonniere, 1987; Bourbonniere, 1989.. In this study, speleothems are treated as soils with unusually high calcite contents, adhering to the traditional operational definitions of soil humic substances. Twenty grams of powdered speleothem were added to 500 ml of Milli-Q w water. Then, sufficient 4 N HCl was added to dissolve the calcite, releasing the humic substances. The pH of the resulting solution was adjusted to approximately 8 with 4 N NaOH so that the HAs would not precipitate. The solution was then split in two equal portions. Both portions were filtered using preweighed Whatman GFrF glass fibre filters Ž0.7 mm. to remove the POM. To examine both the fluorescence and the concentration of the POM, one filter was flushed with Milli-Q w water to remove most of its POM and the other filter was dried in an oven and weighed. After POM removal, both filtrates were recombined for FA–HA separation. POM should not be confused with humin, the other fraction commonly produced when fractionating soil organic matter. For the purposes of this paper, POM is operationally defined as any matter above 0.7 mm and could contain a variety of material such large organic matter Žcolloids. and clays which are in suspension but not necessarily in solution. The P. Õan Beynen et al.r Chemical Geology 175 (2001) 319–341 dissolution of the speleothem calcite requires highly acidic conditions, a situation quite different from the neutral–base conditions of the cave water in which the POM originally reached the speleothem. The acidic solution could promote coagulation of certain organic matter to create compounds that did not exist in the speleothem. Such a situation is unavoidable as the calcite must be dissolved to release organic substances. HAs were precipitated from the recombined filtrate by adjusting the pH to 2. The solution was left to stand for 24 h and was then filtered with Whatman GFrF filters. The filtrate contained organics now operationally defined as FAs. Filters were then rinsed with 0.1 N NaOH to resolubilize the HAs. To collect any extra FAs that may have been trapped with HAs, the HA solution was acidified to pH of 2 and filtered for a second time. This filtrate was then added to the earlier FA solution. The HAs were washed from the second filter with 0.1 N NaOH. All fractions were refrigerated to slow any microbial activity. Ten milliliters of the FA–HA solutions was removed for fluorescence spectroscopy and DOC analysis. The remaining FArHA solutions were then divided; the FAs portion from the three light and three dark speleothem solutions was used for further FA fractionation; and the FA–HA solutions of the remaining six speleothems was recombined and used for size fractionation. The final volume of the solutions for FAs was approximately 800 and 150 ml for the HAs. 4.2. FA fractionation The acid soluble fraction of the organic matter isolated from the speleothems is designated here as the FA fraction ŽpH s 2.. Note that similar to the traditional soil definitions, FAs have undergone no purification other than removal of HAs. Further characterization of the FA fraction according to its sorptive and acid–base character was done using macroporous resin techniques. The primary guide to the procedure used here is the paper by Aiken et al. Ž1992. which used XAD-8 resin to isolate hydrophobic components of DOM and to define the hydrophobic–hydrophilic break, while XAD-4 resin was used to isolate the hydrophilic components. Prior to the application of the resin procedure, FA fractions re- 323 sulting from decalcification of speleothems were diluted with E-Pure w water to reduce their salt content to - 0.5 M, thus reducing their density and eliminating problems observed with floatation of resin beads. Distribution coefficients for dissolved organic acids on XAD resins were shown to be unaffected by salt content up to 0.5 M ŽPietrzyk and Chu, 1977. and these resins have been successfully used to isolate dissolved organics from seawater ŽAiken, 1995.. The FA fraction at pH s 2 is applied first to a column of XAD-8 resin using 36 ml of resinrl of sample. This amount of resin is about 20% more than that recommended by Malcolm Ž1991. for preparative isolations of dissolved aquatic hydrophobic organic matter. Thus, breakthrough of hydrophobic organic components with a kX ) 50 should not have occurred under these conditions according to stringent theoretical considerations ŽMalcolm, 1991.. Adsorption to XAD-8 under these conditions defines organic solutes as hydrophobic in character, while passing through XAD-8 defines hydrophilic organic solutes ŽLeenheer, 1981; Malcolm, 1991; Aiken et al., 1992.. HPOA are eluted from the XAD-8 column with 0.1 N NaOH ŽLeenheer, 1981; Aiken et al., 1992. and those hydrophobic components from the sample that are not eluted with base are termed hydrophobic neutrals ŽHPON. by Leenheer Ž1981.. The effluent from the XAD-8 column contains hydrophilic components and is applied to a column of the same size packed with XAD-4 resin. The hydrophilic components, which adsorb to this resin and are subsequently eluted with 0.1 N NaOH are termed HPIA by Aiken et al. Ž1992.. Not all of the hydrophilic components, which adsorb to XAD-4 are eluted by the base. Those components, which are more strongly held to this resin are thought to bond by p – p interactions with the aromatic matrix of XAD-4 ŽMalcolm and MacCarthy, 1992.. Here, the bound Žnot eluted with 0.1 N NaOH. hydrophilic components are called AXAD-4 AcidsB ŽX4AC., a term used by Malcolm and MacCarthy Ž1992. to mean all of the acids which adsorbed to the XAD-4 resin. Those components, which pass through the XAD-4 resin without binding, are primarily hydrophilic neutrals ŽHPIN. ŽMalcolm and MacCarthy, 1992. but could contain acidic or basic components which were not adsorbed by either column under the stated conditions. Nevertheless, the term HPIN are 324 P. Õan Beynen et al.r Chemical Geology 175 (2001) 319–341 used here to designate this residual, non-adsorbable, fraction. In summary, all of the organic matter contained in the original speleothems is accounted for in the seven operationally defined fractions. The acid or base insoluble organic matter is POM, the base soluble and acid insoluble dissolved organic matter is HA and the acid and base soluble dissolved organic matter is FA. FA can also be fractionated into five sub-fractions: HPOA, HPON, HPIA, X4AC and HPIN. The fluorescence results for the POM, HA, and FA for all the speleothems were compared and the FA sub-fractions were used to indicate the character of the organic components, which percolated through the overlying soil with water and incorporated into the speleothems. 4.3. DOC DOC was determined using a Dohrmann DC-190 Carbon Analyzer with platinum on alumina catalyst at 9008C. Standards and blanks were run daily to determine the system blank which was then used to correct all sample results. Inorganic carbon was first removed from the samples by the carbon analyzer through acidification with 20% H 3 PO4 and by purging with carrier gas Žair.. All dissolved fractions, namely, the bulk FA, bulk HA, HPIA and HPOA, basic and neutral FA, were determined this way. 4.4. Calculation of concentration of organic matter fractions DOC analysis only measured the organic carbon content of the solution, but carbon accounted for ; 51% of the total in soil FAs ŽSFAs. and ; 57% in soil HAs ŽSHAs. ŽSuffett and MacCarthy, 1987; Simpson et al., 1997b.. The origins of the humic substances in the speleothems must be from soils, hence, only soil examples were included in the correction. To provide a more accurate estimate of total organic matter ŽTOM. in the FAs and HAs, these proportions were then used to calculate TOM from the measured DOC values. The TOM now represents the total amount of organic carbon in 20 g of calcite. Finally, all these values Žin mgr20 g calcite. were divided by 20 to convert them to total weight per- centage of organic matter in the calcite for each fraction. Steelink Ž1985. reported slightly different ranges for %C of soil humic substances ŽFAs: 40– 51%; HAs: 54–59%.. While our HA corrections are in an appropriate range, our FA corrections could slightly overestimate the TOM of the FAs, but only by a few percent which is within the measurement error of the DOC analysis. Therefore, they are within "5% of the actual value. POM was measured on the dried preweighed filter paper and the amount doubled because only half the total amount was dried on the filter. The POM concentrations for the fluorescence spectroscopy are reported in parts per million units because they represent the concentration of POM in the immersion oil solution. Half of the total POM was resuspended and homogenized in 10 ml of the immersion oil Ždiscussed below. from which parts per million values could then be calculated. 4.5. Preparation of solid speleothems for absorbance and fluorescence The solid speleothems were cut along their growth axes and finely polished to a thickness of 2 mm " 10% with silicon carbide Žgrain size ; 25–30 mm. to produce smooth surfaces which prevented scattering of the fluorescent excitation beam. Each polished section was taken from the same location in a sample as the 20 g of calcite used for the fractionation work. The strength of the calcite was such that no backing or reinforcement was needed. 4.6. Absorbance spectroscopy Absorbance spectra of the solid speleothems were measured with a Perkin-Elmer UVrVisible Lambda 6 spectrophotometer over the range 200–600 nm to characterize the concentration and nature of organic substances in the speleothems. Pure calcite is known to have negligible absorption in this region ŽMachel et al., 1991.. 4.7. Fluorescence spectroscopy A Perkin-Elmer LS-5 fluorescence spectrophotometer recorded the fluorescence spectrum for P. Õan Beynen et al.r Chemical Geology 175 (2001) 319–341 each solid calcite sample and solution. Slit-widths of 5 nm were used for the monochromators, with a default scan speed of 60 nmrmin. Milli-Q w water ŽDOC ; 0.5 ppm. and the empty cuvette were analyzed each day to test for stability and cleanliness of the apparatus; fluorescence intensity of all tests was within the machine background of 0.1–0.3 units. To allow semi-quantitative comparison of fluorescence intensities between solute samples, sub-samples of the various fractionated, and unfractionated dissolved speleothems, Rhodamine WT dye Ž1 ml of 1 ppm standard. was added to each sample after adjusting the pH to 10. All fluorescence spectra were measured at pH 10 as this provides the best discrimination between organic species, particularly for the FAs from different sources ŽMobed et al., 1996.. The maximum intensity of the Rhodamine WT standard also occurs at pH 10. Rhodamine WT was selected because it is a fairly stable dye and its fluorescence did not interfere with the fluorescence of the organic substances ŽSmart and Laidlaw, 1977.. A blank solution with the dye was used as a standard for fluorescence intensity and all the spiked sample solution intensities normalized to this standard ŽGoldberg and Weiner, 1991.. This procedure compensates for machine drift and intrasample irregularities. Both excitation and emission spectra were measured for all fractions, with numerous scans being made to find the wavelengths of peak excitation and emission. 4.8. Size fractionation The remaining FA–HA speleothem solutions not used as the FA fractionation were recombined and separated according to their molecular sizes by ultrafiltration. The initial size fractionation that had already been made with the POM being removed, hence all the remaining fractions were - 0.7 mm. The addition of the concentrations of the FA and HA fractions provides the Total DOC ŽTDOC. concentrations for each speleothem. An aliquot of 10 ml was removed from the recombined solution for each 100 and 10 kDa centrifuge tube: precleaned MSI centrifuge tubes were used. The tubes were centrifuged until all the solution had passed through the filters. The resulting solutions were then measured for DOC to determine each fractions contribution to 325 the TDOC. The - 1 kDa fraction could not be measured using the centrifuge method and therefore required dialysis using Spectrum Spectra Por 6 dialysis bags. An aliquot of 30 ml of each recombined solution was sealed within the bag and placed in Milli-Q w filtered water. Stirring of the solution facilitated transfer of the - 1 kDa fraction over a 24-h period. The DOC of the Milli-Q w water was measured to ascertain the levels of the - 1 kDa fraction and was corrected for dilution. The subtraction of each progressively smaller fraction from its larger counterpart provided the DOC concentration for the following size divisions: 0.7 mm–100 kDa, 100–10, 10–1, and - 1 kDa. The six speleothems used in this particular analysis covered the colour range from light to dark: Ratsnest Cave ŽRNCP, RNCF2., Crowsnest Pass ŽCNP., McFail’s Cave ŽMF2., Kimberley Ranges ŽWAH., and Ogof Ffynon Ddu ŽOFD.. 4.9. POM fluorescence analysis Because the POM began to settle out in water, Cargille Immersion Oil ŽType FF. was used because its viscosity Ž170 centistokes wcStx. kept the POM in solution and the manufacturer claimed it had virtually no fluorescence. The lowest intensity of the oil was at an excitation wavelength of 350 nm and the emission peak wavelength was well below 400 nm and did not fluoresce in the region where the solid speleothems fluoresced. The analytical procedure was to evaporate the water from the POM, 50% of which was resuspended in the immersion oil and spiked with the dye in the same manner used for the solutions. Fluorescence intensities of the spiked samples were normalized to the fluorescence standard as described above. The solutions were stirred between each fluorescence run to prevent settling of the larger POM particles. 4.10. Neutron actiÕation analysis Trace element concentrations in the speleothems were determined by instrumental neutron activation analysis ŽINAA. in the McMaster University Nuclear Reactor, using a Ge ŽLi. detector Žde Soete et al., 1972; McKlveen, 1981.. The following trace elements were measured: As, B, Ba, Br, Ca, Cl, Co, Cr, 326 P. Õan Beynen et al.r Chemical Geology 175 (2001) 319–341 Dy, Fe, Ga, I, K, La, Mg, Mn, Mo, Na, Nd, S, Sb, Sc, Sm, Ti, Th, U, V, W and Zn. The speleothems were sampled at the same location where the fluorescence was measured. These slices were powdered to homogenize the calcite for the INAA. 5. Results and discussion 5.1. Causes of fluorescence in speleothems The first objective is to ascertain whether humic substances ŽFAs, HAs, and POM. or trace elements are the dominant fluorophore in speleothems. To achieve this aim, fluorescence of the speleothems Žcontaining both humic substances and trace elements. and humic substances extracted from them are compared to humic substance standards and trace element fluorescence spectra. 5.1.1. Standards for organic compounds To provide a comparison for the operationally defined humic and FAs obtained from the speleothems, humic and FAs were extracted from a red oak–white ash forest soil close to the shores of Cootes Paradise, Hamilton, Ontario. Other international standards are available but most are derived from aqueous or peat environments which are not the source of the speleothem organic matter. Due to the varied locations of the speleothems from around the world, no particular soil standard would be more applicable than any other. Therefore, we decided to extract our own humic and FA standards from a forest soil as forests are the most common environment above the samples selected for this study. The extraction procedure followed here is that outlined by Stevenson Ž1982.. Fig. 2a,b shows contour plots of the fluorescence of two humic substance standards, Cootes Paradise SFAs and SHAs, in solution at pH 6.5 and at a concentration of 10 ppm Ždetermined using a Dohrmann DC-190 Carbon Analyzer.. Both standards lack any sharp peaks in either excitation or emission wavelengths. SFAs display two peak excitation wavelengths, at approximately 250–260 nm and 330–340 nm, and one peak emission wavelength at 430 nm. SHAs show a similar but less clear pattern with a peak excitation centred on 250–260 nm and a 430 nm emission peak. The smaller peak centred on 280 nm excitation and 260 nm emission is the Raman peak of water. This is only apparent in the HAs because of their lower fluorescence intensities, which are approximately half that of the FAs; although at the same concentration as SFAs, their HA counterparts fluoresce less strongly. Senesi Ž1990. showed that with increased molecular weight, broadening occurs in the emission peak and there is a decrease in fluorescence efficiency, both of which are attributed to greater proximity of aromatic fluorophores to each other and deactivation of excited states by internal quenching. 5.1.2. Fluorescence of speleothems With this information about the fluorescence of standard humic substances, the fluorescence of the speleothems can now be better understood. Fig. 2c,d shows two examples of the fluorescence fingerprints of solid calcite, CW4, a light-coloured sample from Cold Water Cave and JC11, a dark sample from Jewel Cave. CW4 fluoresces more strongly than JC11 and the two spectra differ quite markedly. JC11 has both longer excitation and emission peak wavelengths. Comparison of the fluorescence of the speleothems with the fulvic and HA standards suggests that there are some similarities between SFAs, SHAs, and CW4. All have centres of peak emission at 430 nm, shown by Miano et al. Ž1988. and Mobed et al. Ž1996. to be indicative of FAs fluorescence. However, the spectrum also resembles that of SHAs. SHAs do not display the distinctive excitation peak of the speleothem samples, but it does share the same emission peak at 430 nm as CW4. The slightly longer wavelength excitation peak of CW4 is probably due to the higher concentration of organic substances in the calcite and its own absorption effect. Mobed et al. Ž1996. describe such an effect and showed that it is caused by inner filtering produced by self-absorbance. At higher concentrations, the incident light is absorbed by the molecules themselves, thereby removing the shorter excitation and emission wavelengths, an effect known as inner filtering or self-absorbance. This effect is most pronounced when the fluorescence spectrum of JC11 is compared. It is a particularly dark calcite presumed P. Õan Beynen et al.r Chemical Geology 175 (2001) 319–341 327 Fig. 2. Fluorescence intensities at excitation and emission wavelengths for Ža. Cootes Paradise SFAs, Žb. Cootes Paradise SHAs, Žc. Cold Water Cave ŽCW4., and Žd. Jewel Cave ŽJC11.. JC11 has different scales on axes. Note the similarity between the SFA and the speleothems’ fluorescent AfingerprintsB. to have high concentrations of organic substances; it displays much longer wavelength excitation and emission peak intensities, with the excitation peak centred on 400 nm and the emission peak at 490 nm. Fig. 3 shows the fluorescence emission spectra of the solid speleothems. They depict very similar spectra, however, there is a clear distinction between the light and dark speleothems, with the lighter speleothems fluorescing more intensely and at shorter wavelengths than the dark samples. Such a result can be explained by the self-absorbance effect described in the previous paragraph. The emission maxima wavelengths are between 430 and 450 nm and longer. A reversal of the solid speleothem results occurs when the speleothems are dissolved. Solutions of the darker speleothems now fluoresce more intensely. It appears that the self-absorbance effect has been diminished because the organic molecules are at lower concentrations in solution than in the solid calcite. Another possible explanation is that POM has been removed and this suggests that it may have had a quenching effect on the speleothems fluorescence. Maximum intensity emission wavelengths are all centred between 410 and 430 nm. In comparison with Ramseyer et al. Ž1997., these wavelengths are shorter by 10–30 nm, yet share the same broad 328 P. Õan Beynen et al.r Chemical Geology 175 (2001) 319–341 Fig. 3. Emission spectra of the various fractions of the speleothems showing the reversal in intensities from solid to liquid phase. The numbered lines correspond to WAH Ž1., RNCP Ž2., MF1 Ž3., CNPLB Ž4., RNCF2 Ž5., CW4 Ž6., MF2 Ž7., OFD Ž8., JC11 Ž9., CNP Ž10., CNPDB Ž11. and RCB Ž12.. Excitation wavelength is 255 nm, except for POM, which is 350 nm. featureless spectral shape. Spectra of the FA fraction are similar to that of the total dissolved organic matter ŽTDOM. solution with common intensity peaks at 425–430 nm, although as with the TDOM, intensities do vary. The darker speleothem FA fraction intensities vary from sample to sample but on average are not stronger than the light coloured speleothems. The TDOM solution fluorescence in- tensities are much greater for the dark speleothems than their light counterparts. The HA fraction possesses a very similar emission to the FA fraction, although its intensities are lower. The POM spectra reveal great variability in both intensity and maximum emission fluorescence wavelengths. To allow easier comparison between the three fluorescing organic components, FAs, HAs, and P. Õan Beynen et al.r Chemical Geology 175 (2001) 319–341 POM, the spectra of the light and dark speleothems were averaged after they had been normalized by dividing the entire spectra’s intensities of each sample by its maximum intensity ŽFig. 4.. The normalization process retains individual sample spectra variability. Fig. 4 shows a comparison of the FA and HA standards with the speleothems; the AlightB and AdarkB lines are the averaged fluorescence spectra for the 12 light and dark speleothems used in this study. Speleothem FAs yield a fluorescence spectrum slightly different from that of Cootes Paradise SFAs, as both the excitation and emission peak wavelengths are shorter. Ramseyer et al. Ž1997. also found that the fluorescence maxima wavelengths from their dissolved speleothems were shorter in comparison with the International Humic Substances Society SFA standard. In the excitation spectra, the dark speleothems show a shoulder between 300 and 350 nm which encompass the peak intensity wavelength Ž330 nm. of SFAs. The light speleothems resemble the dark samples’ excitation spectra. Emission peak intensities are centred between 410 and 420 nm, 20 nm shorter than in the SFAs, which suggests that the cave deposits probably contain smaller molecular weight FAs than the standards. The basis for this suggestion is the work of Senesi Ž1990. who showed that larger organic compounds fluoresced at longer emission wavelengths than smaller organic molecules. The HA fraction of the speleothems ŽFig. 4. behaves similarly in both light and dark calcite to the Cootes Paradise SHAs. They all share the same excitation peak at 255 nm, although the dark samples do not have the same plateau between 300 to 320 nm as do the light samples and SHAs. Emission fluorescence spectra of speleothems and standards are very similar at an excitation of 255 nm, peaking in intensities of approximately 430 nm. However, with an excitation wavelength of 340 nm, the light and dark coloured speleothems differ in maximum emission fluorescence wavelength by 20 nm. Both higher concentrations ŽMobed et al., 1996. or larger organic molecules ŽSenesi, 1990. could account for this difference. The POM fluorescence depicted in Fig. 4 yielded a peak excitation intensity at 350 nm when the emission wavelength was fixed at 430 nm, which is 329 the value of the peak emission obtained from the dissolved speleothems ŽFig. 3.. The shorter excitation wavelengths were not shown because of the very strong excitation peaks observed in the immersion oil used for suspension of the POM. Their strength would totally outweigh that of the POM’s shorter excitation wavelengths. Emission measurements revealed spectra similar to the solid or dissolved samples. POM of both the light and dark calcite shows a peak emission wavelength of approximately 420 nm, which compares well with the 430 nm of the FAs and HAs in the dissolved speleothems. However, the most important feature is the very low fluorescence intensity of the POM and also the broad, featureless form of the emission spectra, producing a white fluorescence. Fluorescence of POM has not been reported in the literature hitherto. If POM is trapped in solid speleothems, in low abundance, it may add to their white fluorescence, but in high concentrations Žas in MF2., fluorescence may also be quenched, due to absorption of UV by the POM. The POM discussed here is simply operationally defined as any material greater than 0.7 mm. It is possible for such large matter to reach a cave in the percolating water. When the authors were working at Marengo Cave in Southern Indiana ŽVan Beynen et al., 1997., the cave waters were filtered in the same manner as the dissolved speleothem calcite and particulate matter was observed on the filters. Velocities of percolating water moving through epikarst can be sufficient to transport matter of this size. 5.1.3. Trace elements The results outlined above strongly suggest that the fluorescence observed in speleothems is dominated by that which originates from organic compounds. Trace and rare earth element concentrations were measured to ascertain if they might contribute to the observed fluorescence. Table 3 reports all those elements, which were detectable in the speleothems. The trace elements are discounted from significant contribution by comparing their published spectra ŽMunoz and Rubio, 1988; W.B. White, 1998, personal communication; O’Donnell et al., 1989; Fujimori et al., 1989; Macler et al., 1989. with fluorescence of speleothems in the present work at concentrations greater than the detection levels. Eu could not be measured by the INAA technique. Eu2q 330 P. Õan Beynen et al.r Chemical Geology 175 (2001) 319–341 Fig. 4. Normalized and averaged excitation and emission spectra for FAs, HAs, and POM extracted from speleothems compared to Cootes Paradise soil FAs rHAs. With the exception of POM, the spectra of the normalized speleothems’ solutions are shorter than the soil standards’ spectra. P. Õan Beynen et al.r Chemical Geology 175 (2001) 319–341 yields an emission peak at 416 nm ŽMachel et al., 1991., close to that of the dissolved speleothems, but its fluorescent spectrum is quite different and hence, it can be discounted as a significant fluorescent contributor. The high concentration of iodine in our samples is of interest in its own right. Ullman and Aller Ž1985. showed that environmental iodine is incorporated by marine organisms and released to accumulating sediments through organic decomposition. It is not surprising that speleothems may incorporate some iodine as their calcite is composed of CaCO 3 derived largely from the overlying rocks. Natural abundances of iodine ŽBecker et al., 1972. have been measured in limestone Ž- 29 ppm., sandstone Ž- 37.6 ppm. and calcareous shale Ž- 38 ppm., all of which are above caves used in this study. 5.1.4. Concentrations of the fractions The above discussion has shown that FAs and HAs are the predominant fluorophores in speleothems, whereas POM probably quenches fluorescence. The next step is to determine which of these two compounds has the higher concentrations and hence, is the dominant fluorophore. Fig. 5a demonstrates each speleothem’s concentrations in mgrg calcite. The most striking feature is the dominance of POM over the FAs and HAs in all speleothems except JC11, RCB, and RNCP. The Table 3 Trace elements present in speleothems Žconcentrations in ppm.. Only values above the detection limit are reported Element Ba Light WAH MF1 CNPLB RNCF2 CW4 60 RNCP Dark MF2 70 OFD JC11 210 RCB CNPDB CNP D.L. 40 Br Cr I Mn Na 0.6 90 310 0.7 30 20 40 220 11 7 0.4 180 110 2 12.8 0.3 10 Abbreviation: D.L. — detection limits. 2 12 1 20 150 70 40 60 40 230 30 240 310 30 40 10 U 0.3 1.5 2.6 0.3 0.7 0.6 0.7 2.0 5.5 0.1 2.1 4.4 0.1 Zn 60 270 30 15 10 840 460 10 331 McFail’s Cave samples and Crows Nest Pass speleothems have particularly high abundances. These high proportional concentrations confirm our suggestion that the POM has a quenching effect on the fluorescence of the speleothems, due to self-absorption, contributing to the lower intensities noted in the solid dark speleothems ŽFig. 3.. However, the lighter speleothems, which fluoresced more strongly in the solid, also display high proportions of POM. Conversely, certain samples tend to have higher relative abundances of FAs, especially RNCP, RCB, OFD and JC11. HAs do not appear to be very prominent, except in CNPDB, CNP, and JC11. The relative abundances of fulvic and humic acids are more clearly displayed in Fig. 5b. Generally, HAs are at least five times less abundant than the FAs. With such a result, this must have important implications for the contribution of HAs to the fluorescence of the speleothems. Although not shown in Fig. 2, SFAs have twice the fluorescence intensity than SHAs measured at the same excitation and emission wavelengths, with both having concentrations of 10 ppm. As FAs have twice the fluorescence at the same concentration as HAs, and the speleothems possess at least five times the quantity of FAs to HAs, then FAs must be the dominant fluorophore due to its concentration. There is also a slightly higher average concentration of organic compounds for the darker speleothems compared to the lighter samples. 5.1.5. Fractionated FA With FAs being the dominant fluorophore, some characterization of what compounds make up this fraction is useful. Of the samples subjected to the FA fractionations, only JC11 and RCB had high enough DOC concentrations to provide meaningful results. Fig. 6 depicts the percentage of TDOC accounted for by the hydrophilic and hydrophobic fractions. Overall, the hydrophilics are much more dominant than the hydrophobics. Such dominance is expected because most of the hydrophobics can be removed from the percolating waters by clay adsorption as they travel through the soil and microfissures in the bedrock ŽThurman, 1985.. For both JC11 and RCB, HPIN is the largest component of the FAs. This fraction could contain acidic, basic, and neutral fractions, but they are all nevertheless highly hy- 332 P. Õan Beynen et al.r Chemical Geology 175 (2001) 319–341 Fig. 5. Ža. POM, FA, and HA concentrations in the speleothems. Žb. Concentrations of FAs and HAs in speleothems. Note the order of magnitude difference in the concentrations of the various fractions. P. Õan Beynen et al.r Chemical Geology 175 (2001) 319–341 333 Fig. 6. Relation between fluorescence intensity Žarbitrary units. and concentration of FAs, HAs, and POM in respective solutions. These are the DOC values of the solutions for the total organic fraction of FAs, HAs, and POC. Shaded triangles are dark speleothems and clear are light samples. drophilic. Such components would be expected to pass through the overlying soil unaffected by adsorption. It is also possible that such components may be secondary products of the microbial degradation of the original organic matter leached from the overlying soil, which could have been hydrophobic or hydrophilic. 5.1.6. Concentration effect on fluorescence Fig. 7 shows the peak fluorescence intensities generated at measured concentrations of FAs, HAs, and POM. Both the FAs and HAs have weak positive relations between intensity and concentration. At low concentrations of the FAs and HAs, a positive correlation between concentration and fluorescence intensity would be expected ŽSenesi, 1990.. More importantly, the FAs and HAs have similar concentrations, however, the FAs generally fluoresce at twice the intensity of the HAs, confirming the Cootes Paradise soil standards result. POM is at much higher concentrations, and the self-absorption effect ŽMobed et al., 1996. is therefore very noticeable with an exponential decay in fluorescence. 5.1.7. Size fractionation Ultrafiltration of the solutions was undertaken to confirm that FAs, the dominant fluorophore as determined by the fluorescence spectroscopy, were also 334 P. Õan Beynen et al.r Chemical Geology 175 (2001) 319–341 Fig. 7. FA fractionation results for JC11 and RCB showing the dominance of the hydrophilic fraction ŽHPIA and HPIN. compared to the hydrophobic fraction ŽHPOA and HPON.. the dominant molecular weight fraction. As noted earlier, FAs typically have molecular weights of 0.8–1 kDa, whereas HAs range from 2 to 300 kDa ŽSuffett and MacCarthy, 1987.. If FAs or smaller organic compounds are the dominant fluorophores, dominance of less than 1 kDa fraction is expected. TDOC values of the six bulk speleothem solutions and their fractions were measured and the percentage composition is shown in Fig. 8. In all the six speleothems, at least 50% of the soluble organic substances have molecular weights less than 10 kDa ŽMWCO.. For RNCP, RNCF2, and OFD the dominant fractions are the FAs Ž- 1 kDa., ranging from 47% to 73% of the TDOC in the speleothems. However, it is not the dominant fraction in the other speleothems. HAs, the 1 kDa to - 0.7 mm fractions, are the dominant components in OFD, WAH, CNP and RNCF2. However, smaller colloids Ž- 0.7 mm. could also be contributing to the 0.7 mm–100 kDa fraction because some have been found to be as small as 0.01 mm and therefore not trapped as POM ŽSposito, 1989.. Their presence may explain why the larger molecular weight fractions are significant in certain speleothems but the HAs are not ŽFig. 5b.. Colloids, once entrained, remain highly mobile and consequently, could be flushed with the organic substances into the cave. 5.2. Causes of colour differences between lighter and darker speleothems 5.2.1. Absorbance spectroscopy Annual laminae in speleothems are delineated by differences in the colour of calcite, whereby a couplet of light and dark calcite indicates a year’s growth. The chemical differences between light and dark calcite is of interest, but their microscopic size makes them difficult to investigate. Bulk samples of calcite will be investigated instead. Although the distinction between light and dark calcite is subjec- P. Õan Beynen et al.r Chemical Geology 175 (2001) 319–341 335 Fig. 8. Molecular weight size fractionations using ultrafiltration with the - 10 kDa fractions accounting for most of the DOM extracted from these speleothems. tive, every attempt was made to distinguish these two groups clearly. Only the McFail’s Cave samples, MF1 and MF2, are from the same cave and yet the former is light and the latter is dark. The samples CNPLB and CNPDB are the only samples to come from one speleothem, which contained thick enough bands of light and dark calcite to provide 20 gm of calcite for analysis. One possible quantitative measure of the difference between light and dark calcite is absorbance. 336 P. Õan Beynen et al.r Chemical Geology 175 (2001) 319–341 Absorption spectra ŽFig. 9. show the expected higher absorbance of darker speleothems in the visible region and correspondingly, the high absorbance in the near UV. The chromophores, responsible for visible darkening of the speleothems, also absorb much of the incident UV, reducing fluorescence through selfabsorption effects. Absorbance maxima for the speleothems range from 240 to 300 nm. Such wavelengths, particularly between 270 and 280 nm, are typical of electron transitions for phenolic substances, aniline derivatives, benzoic acids, polyenes and polycyclic aro- matic hydrocarbons ŽBraun et al., 1988.. Some of these are expected components of humic substances and have been shown to cause fluorescence in speleothems, it was anticipated that the peak intensities would occur at these wavelengths. Fig. 10a shows the correlation between absorbance and TOM ŽTOM s FAs q HAs q POM.. This parameter was chosen because it is not clear which of the three organic components of the speleothem would be most responsible for the absorption. There is a weak positive correlation, therefore, TOM could be considered a reasonable proxy Fig. 9. Absorbance spectra for the speleothems demonstrate the longer absorbance maxima wavelengths of the dark speleothems which are centred around 300 nm compared with the 240–260 nm of the light speleothems. The same numbers as Fig. 3 are used for the speleothems. P. Õan Beynen et al.r Chemical Geology 175 (2001) 319–341 337 Fig. 10. Relations between maximum absorbance value of the solid speleothems Žtaken from Fig. 9. and their corresponding Ža. TOM, Žb. POM, Žc. FA and Žd. HA concentrations. Shaded circles are dark speleothems and clear are light samples. There is a potential that the higher absorbances Ždarker colours. could be attributed to augmented organic concentrations. for absorbance and colour. However, dark speleothems are not consistently higher in TOM ŽFig. 5a.. Fig. 10b–d demonstrates the relation between absorbance and FAs, HAs, and POM concentrations. It is not immediately apparent which fraction is most responsible for absorption Žcolour. because they all resemble the TOM distribution shown in Fig. 10a. However, the POM fraction resembles the TOM most closely, not surprisingly since, in most speleothems, POM is the dominant species and therefore is probably the principal chromophore. Having viewed the colour of the POM and the colour of the speleothems, it is our view that there was a great similarity between them. While it is true that the FA and HA fractions also possessed similar colours to their parent speleothems, their concentrations were orders of magnitude lower than the POM. While there is little similarity between the fluorescence spectra of the POM ŽFig. 4. and the solid speleothems, it must be remembered that the wavelengths of excitation were different, but more importantly, that the POM was in a much higher concentration when its fluorescence properties were measured than what it would have been in the speleothem. Therefore, the inner filtering effect ŽMobed et al., 1996. created by the high levels of POM would alter the fluorescence spectra. Some other characterization of POM could be useful to determine what this component represents. P. Õan Beynen et al.r Chemical Geology 175 (2001) 319–341 338 To this end, loss on ignition ŽLOI. analysis was undertaken on the POM to determine the proportions of organic to inorganic matter. The LOI procedure followed was that outlined by Hesse Ž1971.. Whatman w QM-A Quartz filters were used to remove the POM from solution. The filters were then dried at 1058C for 1 h to remove moisture and weighed to determine the total POM. The filters were then ignited in a preheated furnace at 9508C for 1 h to remove the organic matter from the samples and weighed once more. The quartz filters were selected because they could withstand the high furnace temperatures required to ignite the organics. Three blanks were put through the same process and retained their integrity though the mean weight loss was added to the final filter weight of the samples. The results of this experiment are shown in Table 4. There is great variability in the contribution of organic matter to the POM fraction, ranging from 0% to 66%. Consequently, the only conclusions that can be drawn are that the ashrclay content was significant, making up at least 34% of the total POM. In appearance, the inorganic component seemed to be fine clay, though the difficulty of extracting this material from the filters discouraged any further identification. Clay does bind organic matter and therefore, it must be assumed that some of the fluorescence measured in the POM fraction could have been contributed by organic molecules bound to the clay. 5.2.2. Size separations The size separation results also give an indication of the different size concentrations of the various light and dark coloured speleothems. Distinctions are made difficult by the small sample size and the lack of total unanimity between the light and dark samples as seen in Fig. 8. Not all 12 samples could be Table 4 Percentage organic matter in POM as derived from LOI analysis. Only these six samples were analyzed Sample % Organic matter CNP MF2 OFD RNCF2 RNCP WAH 37.2 61.7 44.8 0.0 0.0 66.0 analyzed as the other six speleothems were used for the FA fractionation. For the light samples, RNCP and RNCF2 both show the dominance of the smallest fraction, - 1 kDa, while OFD and CNP both show higher concentrations of the larger molecular weight fractions. These larger molecular weight fractions are probably the HAs, and it was shown in Fig. 5 that the darker speleothems have on average a higher concentration of HAs. Regarding the two smallest size categories Ž- 1–10 kDa., it appears that all the speleothems have similar proportions ranging from 60% to 75% of the total soluble organic matter, with the exception of MF2. 5.3. ReactiÕities of organic matter with calcite Certain organic compounds have high affinities for sorption on calcite ŽSuess, 1970; Carter, 1978; Reynolds, 1978.. These variable affinities can lead to either promotion ŽSuess, 1970. or inhibition of calcite precipitation ŽReynolds, 1978.. If certain substances, such as polyphenols, will preferentially bind with the calcite and others not, then, this will make the fluorescence and colour of speleothems differ in comparison with that of the organic assemblages that exist in the percolation waters and consequently, those of the environment above the cave. In an earlier paper ŽVan Beynen et al., 2000., we found however, that percolation waters’ fluorescent properties are identical to those of the speleothems measured in this paper. The evidence suggests that any selective binding of specific organic species on the calcite is of minor influence in determining the organic content of the speleothem. The prior observations of the drip waters together with work presented here, suggests all of the organics in the cave waters are incorporated in the speleothems because of the macromolecular nature of the organics. While certain organic components of the macromolecule may not possess an affinity to bind with calcite, other components of the molecule do, thereby binding the entire macromolecule to the calcite crystal. 5.4. Comparison of CNPLB and CNPDB Only one speleothem offered thick enough bands to compare light and dark calcite, CNPLB and CNPDB. Both came from the same sample, but not from P. Õan Beynen et al.r Chemical Geology 175 (2001) 319–341 CNP, which was an entirely different speleothem but which acts as a control. The reason for the difference in the appearance of the calcite appears to be the four times higher concentration of HAs in the dark band compared to the light ŽFig. 5b., as both have similar POM and FA concentrations ŽFig. 5a.. This speleothem has two thick pairs of light and dark bands, suggesting that twice during its growth, there was a switch from high to low HA concentrations. Such a transition must reflect a changing environment above the cave but these phases have not been dated. CNPDB exhibits much stronger fluorescence than CNPLB in the HA solution fraction. There are no other differences between these two portions of the speleothem. This has important implications for the difference between light and dark calcite, which comprises annual bands in calcite. CNP has slightly higher POM levels than CNPDB and CNPLB, but more importantly like CNPDB, CNP is a dark speleothem and also has high levels of HAs. 6. Conclusions The purpose of this study was to investigate the relation between organic constituents in speleothems and their fluorescence and colour. It appears that fluorescence is caused by humic substances and not trace elements. FAs have higher fluorescent yields Žper ppm. than HAs, but more significantly because of their higher relative concentration, appear to be the dominant contributor to fluorescence. The HPIN components in FAs are dominant, followed by the HPIA. The POM in the speleothems may have a quenching effect on the fluorescence, a finding suggested by the reversal of fluorescent intensities of light and dark calcite once the POM was removed by dissolution of the speleothem. However, the enhanced fluorescence can also be caused by the dilution of the FAs–HAs that in the solid calcite absorbed a great deal of the fluorescence. Average organic concentrations Žin 1 gm of calcite. in the speleothems are as follows: POM — 204 ppm, FAs — 0.893 ppm, and HAs — 0.064 ppm. These results show that some darker calcites possess higher concentrations of humic substances, but fluoresce less strongly than lighter calcite due to the 339 higher abundances in the dark calcite of the POM and its associated fluorescent quenching. Some dark speleothems also contain larger, more complex organic substances ŽHAs. as well as the simpler compounds ŽFAs. of the lighter calcite. Extrapolating these findings to the interpretation of annual laminae in speleothems, periods of high organic concentrations in cave feedwater will produce low fluorescence in the solid speleothem, such as late winter and the spring when humic substances are flushed from the soil ŽVan Beynen et al., 1997. due to self-absorbance or quenching. Conversely, periods of low concentrations will yield high fluorescence in the speleothem, such as the summer and fall. Therefore, the presence of annual bands can be determined using fluorescence microscopic photography. Multiple speleothems from two caves ŽRatsnest and McFail’s. exhibited some differences in behaviour, a result that can best be explained by the nature of the epikarst above the cave which can produce different flow paths and soil thicknesses above the speleothems. However, the Crows Nest Pass speleothems were quite similar. Comparison of light and dark calcite from this cave showed that dark calcite ŽCNPDB. contained more HAs than the light calcite ŽCNPLB., a result which strengthens arguments about the chemical differences between light and dark calcite. Acknowledgements We greatly appreciate the technical help of George Timmins, Scott Smith, Karen Edmondson and Alice Pidruczny. This research was funded by an operating grant to Ford from the National Sciences and Engineering Research Council of Canada. References Aiken, G.R., McKnight, D.M., Thorn, K.A., Thurman, E.M., 1992. Isolation of hydrophilic organic acids from water using nonionic macroporous resins. Org. Geochem. 18, 567–573. Aiken, G.R., 1995. Isolation and concentration techniques for aquatic humic substances. In: Aiken, G.R., McKnight, D.M., Wershaw, R.L., MacCarthy, P. ŽEds.., Humic Substances in Soil, Sediment, and Water. Wiley, New York, pp. 363–385. 340 P. Õan Beynen et al.r Chemical Geology 175 (2001) 319–341 Baker, A., Smart, P.L., Richards, A., 1993. Annual growth bandings in a cave stalagmite. Nature 272, 24–28. Baker, A., Genty, D., Smart, P.L., 1998. High-resolution records of soil humification and paleoclimate change from variations in speleothem luminescence excitation and emission wavelengths. Geology 26, 903–906. Becker, V.J., Bennett, J.H., Manuel, O.K., 1972. Iodine and uranium in sedimentary rocks. Chem. Geol. 9, 133–135. Bourbonniere, R.A., 1989. Distribution patterns of dissolved organic matter fractions in natural waters from eastern Canada. Org. Geochem. 14, 97–107. Braun, D.W., Floyd, A.J., Sainsbury, M., 1988. Organic Spectroscopy. Wiley, New York, pp. 3–23. Broecker, W.S., Olsen, E.A., Orr, P.C., 1960. Radiocarbon measurements and annual rings in cave formations. Nature 185, 93–94. Carter, P.W., 1978. Adsorption of amino acid-containing organic matter by calcite and quartz. Geochim. Cosmochim. Acta 42, 1239–1242. Clapp, C.E., Hayes, M.H.B., 1999. Sizes and shapes of humic substances. Soil Sci. 164, 777–789. de Soete, D., Gijbels, R., Hoste, J., 1972. Neutron Activation Analysis. Wiley, New York. Dorale, J.A., Gonzalez, L.A., Reagan, M.K., Pickett, D.A., Murell, M.T., Baker, R.G., 1992. A high resolution record of Holocene climate change in speleothem calcite from Cold Water Cave, northeastern Iowa. Science 258, 1626–1630. Ertel, J.R., 1988. Genesis: group report. In: Frimmel, F.H., Christman, R.F. ŽEds.., Humic Substances and Their Role in the Environment. Wiley, New York, pp. 105–112. Fujimori, H., Matsui, T., Suzuki, K., 1989. Simultaneous determination of U and HNO 3 concentrations in solution by laser induced fluorescence spectroscopy. J. Nucl. Sci. Technol. 25, 798–804. Gascoyne, M., 1977. Trace element geochemistry of speleothems. Proc. 7th Int. Speleo. Cong., Sheffield, England. pp. 205–208. Gascoyne, M., 1992. Paleoclimatic determination from cave calcite deposits. Quat. Sci. Rev. 11, 609–632. Genty, D., Quinif, Y., 1996. Annually laminated sequences in the internal structure of some Belgian stalagmites — importance for paleoclimatology. J. Sediment. Res. 66, 275–288. Gilson, J.R., MacCarthney, E., 1954. Luminescence in speleothems from Devon, UK: the presence of organic activators. Ashford Speleol. Soc. J. 6, 8–11. Goldberg, M.C., Weiner, E.R., 1991. Fluorescence spectroscopy in environmental and hydrological sciences. In: Wolfbeis, O.S. ŽEd.., Fluorescence Spectroscopy: New Methods and Application. Springer-Verlag, New York, pp. 213–241. Hayase, K., Tsubota, H., 1985. Sedimentary humic acid and fulvic acid as fluorescent organic materials. Geochim. Cosmochim. Acta 49, 159–163. Hesse, P.R., 1971. A Textbook of Soil Chemical Analysis. Chemical Publishing, New York, p. 210. Lauritzen, S.E., Ford, D.C., Schwarcz, H.P., 1986. Humic substances in speleothem matrix, paleoclimate significance. Proc. 9th Int. Cong. Speleology, Barcelona, Spain. pp. 77–79. Leenheer, J.A., 1981. Comprehensive approach to preparative isolation and fractionation of dissolved organic carbon from natural waters and waste waters. Environ. Sci. Technol. 15, 578–587. Leenheer, J.A., 1985. Fractionation techniques for aquatic humic substances. In: Aiken, G.R., McKnight, D.M., Wershaw, R.L., MacCarthy, P. ŽEds.., Humic Substances in Soil, Sediment, and Water. Wiley, New York, pp. 409–429. Li, W., Lundberg, J., Dickin, A.P., Ford, D.C., Schwarcz, H.P., Williams, D., 1989. High precision mass-spectrometric Useries dating of cave deposits and implications for paleoclimate studies. Nature 339, 534–536. Machel, H.G., Mason, R.A., Mariano, A.N., Mucci, A., 1991. Causes and emission of luminescence in calcite and dolomite. In: Barker, C.E., Kopp, O.C. ŽEds.., Luminescence Microscopy and Spectroscopy. SEPM, pp. 9–25. Macler, M., Nicolai, J.P., Heaven, M.C., 1989. Electronic spectroscopy and energy transfer pathways for matrix isolated iodine. J. Chem. Phys. 91, 365–373. Malcolm, R.L., 1991. Factors to be considered in the isolation and characterization of aquatic humic substances. In: Boren, H., Allard, B. ŽEds.., Humic Substances in the Aquatic and Terrestrial Environment. Wiley, London, pp. 369–391. Malcolm, R.L., MacCarthy, P., 1992. Quantitative evaluation of XAD-8 and XAD-4 resins used in tandem for removing organic solutes from water. Environ. Int. 18, 597–607. Mason, R.A., Mariano, A.N., 1990. Cathodoluminescence activation in manganese-bearing and rare earth-bearing synthetic calcite. Chem. Geol. 88, 191–206. McKlveen, J.W., 1981. Fast Neutron Activation Analysis. Ann Arbour Sci. Publ. Miano, T.M., Sposito, Martin, J.P., 1988. Fluorescence spectroscopy of humic substances. Soil Sci. Soc. Am. J. 52, 1016–1019. Mitterer, R.M., 1968. Amino acid composition of organic matrix in calcareous oolites. Science 162, 1498–1499. Mobed, J.J., Hemminsen, S.L., Autry, J.L., McGown, L.B., 1996. Fluorescence characterization of IHSS humic substances: total luminescence spectra with absorbance correction. Environ. Sci. Technol. 30, 3061–3065. Munoz, F.F., Rubio, O.J., 1988. Fluorescence of tin sensitized Mn in single-crystalline NaCl. Phys. Rev. B 38, 9980–9986. O’Donnell, K.P., Marshall, A., Yamaga, M., Henderson, B., 1989. Vibronic structure in the photoluminescence spectrum of Cr 3q ions in garnets. J. Lumin. 42, 365–373. Pietrzyk, D.J., Chu, C., 1977. Amberlite XAD copolymers in reversed phase gravity flow and high pressure liquid chromatography. Anal. Chem. 49, 757–763. Ramseyer, K., Miano, T.M., D’Orazio, V., Wildberger, A., Wagner, T., Geister, J., 1997. Nature and origin of organic matter in carbonates from speleothems, marine cements and coral skeletons. Org. Geochem. 26, 361–378. Reynolds, R.C., 1978. Polyphenol inhibition of calcite precipitation in Lake Powell. Limnol. Oceanogr. 23, 585–597. Richmond, M., Bourbonniere, R.A., 1987. Manual for the fractionation of dissolved organic matter in natural waters. NWRI Report 87-145, Environment Canada, Ottawa, p. 29. Schlesinger, W.H., 1977. Carbon balance in terrestrial detritus. Ann. Ecol. Syst. 8, 51–81. Schwarcz, H.P., 1986. Geochronology and isotopic geochemistry P. Õan Beynen et al.r Chemical Geology 175 (2001) 319–341 of speleothems. In: Fontes, J.C., Fritz, P. ŽEds.., Handbook of Environmental Isotope Geochemistry. The Terrestrial Environment, B. Elsevier, Amsterdam, pp. 271–303. Senesi, N., 1990. Molecular and quantitative aspects of the chemistry of fulvic acid and its interactions with metal ions and organic chemicals. Anal. Chim. Acta 232, 77–106. Senesi, N., Miano, T.M., Provenzano, M.R., Brunetti, G., 1991. Fluorescence spectroscopy of humic substances. Soil Sci. Soc. Am. J. 52, 1016–1019. Shopov, Y.Y., Dermendjiev, V., Buyukliev, G., 1989. Investigation on the variations of climate and solar activity by a new method — LLMZA of cave flowstone from Bulgaria. Proc. 10th Int. Cong. Speleology, Budapest, Hungary, pp. 95–97. Shopov, Y.Y., Ford, D.C., Schwarcz, H.P., 1994. Luminescence microbanding in speleothems: high resolution chronology and paleoclimate. Geology 22, 407–410. Simpson, A.J., Burdon, J., Graham, C.L., Hayes, M.H.B., 1997a. Humic substances from podzols under oak forest and cleared forest site: II. Spectroscopic studies. In: Hayes, M.H.B., Wilson, W.S. ŽEds.., Humic Substances, Peats, and Sludges: Health and Environmental Aspects. Royal Society of Chemistry, Cambridge, pp. 83–92. Simpson, A.J., Watt, B.E., Graham, C.L., Hayes, M.H.B., 1997b. Humic substances from podzols under oak forest and cleared forest site: I. Isolation and characterization. In: Hayes, M.H.B., Wilson, W.S. ŽEds.., Humic Substances, Peats, and Sludges: Health and Environmental Aspects. Royal Society of Chemistry, Cambridge, pp. 73–82. Smart, P.L., Laidlaw, I.M.S., 1977. An evaluation of some fluorescent dyes for water tracing. Water Resour. Res. 13, 15–33. Sposito, G., 1989. The Chemistry of Soils. Oxford, New York, p. 188. Steelink, C., 1985. Implications of elemental characteristics of humic substances. In: Aiken, G.R., McKnight, D.M., Wershaw, R.L., MacCarthy, P. ŽEds.., Humic Substances in Soil, Sediment, and Water. Wiley, New York, pp. 457–476. Stevenson, F.J., 1982. Humus Chemistry. Wiley, New York, 443. Stevenson, F.J., 1985. Geochemistry of soil humic substances. In: Aiken, G.R., McKnight, D.M., Wershaw, R.L., MacCarthy, P. ŽEds.., Humic Substances in Soil, Sediment, and Water. Wiley, New York, pp. 14–51. Suess, E., 1970. Interaction of organic compounds with calcium 341 carbonate-I. Association phenomena and geochemical implications. Geochim. Cosmochim. Acta 34, 157–168. Suffett, I.H., MacCarthy, P., 1987. Aquatic Humic Substances. ACS, Washington, xxiii. Swift, R.S., 1985. Fractionation of soil humic substances. In: Aiken, G.R., McKnight, D.M., Wershaw, R.L., MacCarthy, P. ŽEds.., Humic Substances in Soil, Sediment, and Water. Wiley, New York, pp. 387–408. Terakado, Y., Masuda, A., 1988. The coprecipitation of rare-earth elements with calcite and aragonite. Chem. Geol. 69, 103–110. Thurman, E.M., 1985. Humic substances in groundwater. In: Aiken, G.R., McKnight, D.M., Wershaw, R.L., MacCarthy, P. ŽEds.., Humic Substances in Soil, Sediment, and Water. Wiley, New York, pp. 87–103. Ullman, W.J., Aller, R.C., 1985. The geochemistry of iodine in near-shore carbonate sediments. Geochim. Cosmochim. Acta 49, 967–978. Van Beynen, P.E., Ford, D.C., Schwarcz, H.P., 1997. Characterization and seasonality of humic substances in Cave Water, Marengo Cave, Indiana. Proc. 12th Int. Cong. Speleology, La Chaux de Fonds, Switzerland, p. 262. Van Beynen, P.E., Ford, D.C., Schwarcz, H.P., 2000. Seasonal variations in organic substances in surface and cave waters at Marengo Cave, Indiana. Hydrol. Proc. Žin press.. Visser, S.A., 1983. Fluorescence phenomena of humic matter of aquatic origin and microbial cultures. In: Christman, R.F., Gjessing, E.T. ŽEds.., Aquatic and Terrestrial Humic Materials. Ann Arbor Sci. Publ., Ann Arbor, MI, pp. 183–202. Wershaw, R.L., Aiken, G.R., 1985. Molecular weights of humic substances. In: Aiken, G.R., McKnight, D.M., Wershaw, R.L., MacCarthy, P. ŽEds.., Humic Substances in Soil, Sediment, and Water. Wiley, New York, pp. 409–429. White, W.B., Brennan, E.S., 1989. Luminescence of speleothems due to fulvic acid and other activators. Proc. 10th Int. Cong. Speleology, Budapest, Hungary, pp. 212–214. White, W.B., 1997. Precise measurement of luminescence banding profiles in speleothems for paleoclimatic interpretation. Proc. 12th Int. Cong. Speleology vol. 1. La Chaux de Fondes, Switzerland, pp. 89–92. Wilson, M.A., Collin, P.J., Malcolm, R.L., Perdue, E.M., Cresswell, P., 1988. Low molecular weight species in humic and fulvic fractions. Org. Geochem. 12, 7–12.
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