Photoluminescence Spectra of Emeralds from Colombia, Afghanistan, and Zambia
ABSTRACT
Laser-excited photoluminescence spectra were collected from 48 emeralds originating from Colombia, Afghanistan, and Zambia. Photoluminescence in emerald arises from trace chromium impurities, and its spectrum displays two narrow R lines overlaid upon a broadband signal. In the collected spectra, peak positions of these R lines varied across a small range of wavelengths; the origin-dependent nature of these variations may be helpful in identifying the geographic source of unknown samples. Comparisons between R-line peak wavelengths and corresponding trace element concentrations of samples revealed strong correlations between peak shifts of the R1 line and increases in magnesium and sodium concentrations, and between peak shifts of the R2 line and increases in lithium and sodium concentrations. These correlations suggest that substitution defects of magnesium for aluminum with sodium impurities may be responsible for the R1 line peak shifts, and similar defects of lithium for beryllium with sodium impurities may be responsible for the R2 line peak shifts. Finally, a comparison between photoluminescence count rates and chromium and iron concentrations showed that count rates decrease exponentially with increasing iron concentration.
INTRODUCTION
Emerald (figure 1) is a gem variety of beryl (Be3Al2Si6O18), whose green color arises from trace impurities of chromium and/or vanadium. While pure beryl is colorless, the trace amounts of Cr and V ions absorb light in the red and blue-violet region of the visible spectrum to produce emerald’s green color (Schwarz and Schmetzer, 2002). Emeralds may also contain trace amounts of iron; this chromophore ion, also responsible for colors seen in the heliodor and aquamarine varieties of beryl (Nassau, 1978), may add a yellow or blue tint.
Some of the visible light energy absorbed by emerald’s Cr ions can reappear as red photoluminescence (Nassau, 1978). This photoluminescence (PL) is usually not bright enough to be seen under normal lighting conditions. Illuminating an emerald with green monochromatic laser light produces a PL reaction that can be observed when the excitation light is blocked by a color filter (figure 2). Laser-excited PL spectra of emerald (figure 3) contain a broadband structure, peaking at about 715 nm, that results from a Stokes-shifted reversal of the electron transition that produces emerald’s red absorption band (Lai, 1987). Superimposed upon this structure are two narrow lines that arise from electronic decay of a doublet metastable state, known as R lines (Wood, 1965). These R lines also appear in emerald absorption spectra, where the longer-wavelength line (denoted R1) peaks at around 683 nm and the shorter-wavelength line (R2) peaks at around 680 nm (Wood, 1965).
Moroz et al. (2000) collected PL spectra from natural emeralds from nine deposits, as well as from a synthetic emerald. In their PL spectra, the peak positions of the R lines of emeralds from schist-host deposits showed moderate shifts in wavelength compared to those lines from emeralds originating from other types of deposits. The authors suggested that these wavelength shifts might be caused by Mg or Fe ions substituting at Al sites, based on the principle that these impurities occur at higher concentrations in schist-origin emeralds.
Recently, Thompson et al. (2014) collected PL spectra of natural emeralds from 11 different localities and synthetic emeralds from four different sources. The results confirmed observations made by Moroz et al. (2000): R1 lines of synthetic emeralds peak at the shortest wavelengths, while in natural non-schist emeralds this line peaks at the same or longer wavelengths. In schist-origin emeralds the line peaks at an even longer wavelength, with peak positions spread across a range on the order of 1.0 nm. By comparison, the spread of R2 lines of most emeralds fell within a 0.2 nm range, though some schist-origin emeralds had R2 lines shifted up to 0.3 nm outside this range toward shorter wavelengths.
Thompson et al. (2014) compared their natural emeralds’ R1-line wavelengths to chemical composition measurements of a different set of emeralds with the same origin, and observed correlation between R1-line wavelengths and SiO2 weight concentrations. The authors suggested that R1 line shifts might arise from impurity substitutions at Si crystal sites in emerald. This speculation was incorrect, as an earlier X-ray diffraction study of beryl (Aurisicchio et al., 1988) found no evidence for substitution defects occurring at Si crystal sites in any type of natural or synthetic beryl. Schmetzer and Bernhardt (1994), and more recently Schmetzer (2015), showed that the minor reductions in Si weight concentrations in emerald could arise from an accrual of substitutions at Al crystal sites.
While Aurisicchio et al. (1988) found no ion substitutions at Si tetrahedral sites in beryl, they examined the other beryl crystal cation sites and did find that two types of substitutions can occur at Al octahedral sites. One is isovalent substitution, where the Al ion is replaced by another trivalent cation. Using Schmetzer’s (2015) notation, this substitution can be written as
The other type is an aliovalent substitution, where the Al ion is replaced by a divalent cation. This substitution is accompanied by an alkali ion to provide charge compensation, where the alkali ion occupies an interstitial site within the beryl’s open channels parallel to the c-axis (Goldman et al., 1978). This substitution can be written as
Only a single substitution is possible at the tetrahedral site, the aliovalent substitution:
Here the Be ion is replaced by a Li ion, accompanied by another alkali ion occupying an open channel site to provide charge compensation. While Aurisicchio et al. found that this substitution is common in some varieties of beryl, they did not observe significant occurrence of this substitution in emerald.
Saeseaw et al. (2014) performed microscopic, spectroscopic, and trace element analysis of emeralds with three-phase inclusions. Here we examine their samples from Colombia, Afghanistan, and Zambia. These samples are of interest because of the different geologies in which they formed. Colombian emeralds formed through hydrothermal processes in sedimentary shale, whereas Zambian emeralds are found in metamorphic phlogopite schists. The Afghan emeralds are hosted in metamorphic-metasomatic phlogopite schists subjected to strong hydrothermal processes (Groat et al., 2008; Giuliani et al., 2012). In short, Afghan emerald formed in a process similar to that which formed Colombian emeralds, but within host material similar to Zambian emeralds. As a result, the Colombian and Zambian emeralds exhibit distinctly different concentrations of several trace impurities, while impurity concentrations in Afghan emeralds bridge these two extremes (Saeseaw et al., 2014).
This study expands upon the work of Thompson et al. (2014) and presents R-line peak wavelength results derived from PL spectra of 48 Colombian, Afghan, and Zambian emerald samples prepared by GIA’s laboratory in Bangkok; most of these samples were also used in Saeseaw et al. (2014). The present study demonstrates that the accumulation of R-line peak wavelength data from samples of known origin can provide evidence for or against various geographic origins. The peak wavelength data are compared with the samples’ trace impurity concentrations to identify which trace impurities might be responsible for shifting R-line peak wavelengths. The study concludes with a comparison between Cr and Fe concentrations and broadband PL emission intensity to quantify the role each element plays in emerald photoluminescence.
MATERIALS AND METHODS
We collected PL spectra from 48 emerald samples on loan from GIA’s Bangkok laboratory. Twenty of the samples were from the Coscuez and Muzo mines in the Boyacá region of Colombia, separated by about 10 km; 16 samples from two mines, Kameer Safeed and Koskanda, in the Khendj area of Afghanistan’s Panjsher region, separated by less than 1 km; and 12 samples from the Kagem mine in the Kafubu area of Zambia. Forty-five of these samples were used in the work by Saeseaw et al. (2014), while one Afghan sample and two Zambian samples were used for the first time in this report. As outlined by Saeseaw et al. (2014), GIA altered its emeralds from their original rough form by polishing one or two flat surfaces perpendicular to each crystal’s c-axis; some also have flat surfaces polished parallel to the c-axis. A specialized tool designed to locate the c-axis of a specimen (Thomas, 2009) was used to align the samples for polishing these flat surfaces.
As Saeseaw et al. (2014) describe, GIA’s Bangkok laboratory determined the chemical composition of each emerald sample using laser ablation–inductively coupled plasma–mass spectrometry (LA-ICP-MS). For quantitative analysis, the spectrometer was calibrated using NIST 610 and 612 glasses with known concentrations of elements. Along with providing the emerald samples, GIA also supplied their chemical composition measurements (table 1).
TABLE 1. Chemical composition of emerald samples (ppma), as measured by LA-ICP-MS. | |||
Colombia | Afghanistan | Zambia | |
7Li | 90–345 (173) |
225–596 (301) |
1280–2323 (1704) |
9Be | 91,359–118,638 (108,826) |
96,325–120,710 (107,886) |
90,388–122,046 (106,214) |
23Na | 1037–6730 (3382) |
4621–10,646 (8053) |
11,482–14,262 (13,365) |
24Mg | 1021–6076 (3034) |
3683–10,070 (7299) |
9804–13,946 (11,762) |
27Al | 57,790–75,526 (66,762) |
53,057–70,257 (62,230) |
48,171–62,381 (55,249) |
Si normalized value |
(206,897) | (206,897) | (206,897) |
39K | 0–13 (3) |
63–612 (316) |
172–300 (243) |
45Sc | 2–83 (30) |
27–880 (225) |
6–41 (19) |
51V | 116–1731 (618) |
93–1264 (488) |
30–72 (42) |
53Cr | 83–677 (295) |
79–1432 (651) |
357–1427 (924) |
57Fe | 69–723 (219) |
380–3153 (1439) |
2252–3834 (3069) |
133Cs | 1–2 (1) |
3–12 (7) |
0–207 (149) |
Analyses were performed at GIA’s Bangkok lab. Data are reported in minimum and maximum values, with average concentration in parentheses, and assume ideal oxygen concentration of 535,782 ppma. Alkali and transition metals with less than 25 ppma for all samples are not included in the table.
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The experimental setup for collecting PL spectra (figure 4) has been described previously (Thompson et al., 2014). A continuous-wave diode pumped solid state (DPSS) laser (Laserglow LRS-532-TM-100-10) emits a 100 mW, 532 nm beam with horizontal polarization. Then a 0.5 mm diameter optical fiber with a 25° field-of-view collimating lens, mounted perpendicular to the laser beam, collects PL emission at room temperature from an emerald sample placed within the overlap region between the laser beam and collection lens field of view. The PL emission collected by the fiber enters a charge-coupled device (CCD) spectrometer (Ocean Optics USB4000) with a custom grating that disperses light over the 580–740 nm wavelength range; this spectrometer has full width at half maximum (FWHM) resolution of 0.20 nm, and the average width of each spectrometer channel is 0.045 nm. Discrete line emissions from argon and neon spectral lamps were used to calibrate the spectrometer’s wavelength scale.
For this study, one change was made to the previous setup: A vacuum pen (Dazor SPK-100-VPEN) was used to position the emeralds. The pen’s pulley system allows complete rotation of the sample about an axis through the stone. The pen itself is held in another rotation mount to allow rotation of the sample about a second, orthogonal axis. In turn, the rotation mount is attached to an XYZ translation stage with at least 13 mm of travel in three orthogonal directions. This assembly provides fine control for positioning a sample so that the laser beam can intersect any point along its surface (not obscured by the pen’s vacuum suction cup) at any incident angle.
Emerald is optically uniaxial, and PL emission spectra collected when the excitation laser beam’s polarization axis is perpendicular to the crystal’s c-axis (E⊥c) differ from those collected with the beam’s polarization axis parallel to the c-axis (E׀׀c). Both R1 and R2 peak positions change, as does the R1/R2 peak height ratio, as described in box A. Emeralds from different localities show the largest quantitative variations for these peak parameters when the spectra are collected with E⊥c beam-crystal axes orientation. Therefore, the current study only considers spectra collected with E⊥c beam-crystal axes orientation.1
To collect a PL spectrum with E⊥c orientation, the sample itself is positioned so that the excitation laser beam enters a flat surface polished perpendicular to the crystal’s c-axis at normal incidence. With this orientation, the excitation laser beam’s polarization axis is also perpendicular to the crystal’s c-axis. The sample is always positioned so that the beam overlaps the emerald edge closest to the optical fiber’s collection lens (again, see figure 4). This sampling position was chosen to minimize PL emission traveling through unilluminated emerald before entering the fiber.
To construct each sample’s PL spectrum, 100 accumulated scans were averaged; each scan’s typical integration time was one second. In a similar manner, with the laser shuttered, a “dark” spectrum was produced. The final PL spectrum was created by subtracting the so-called dark spectrum from the sample spectrum. Doing so reduced counting noise arising from thermal motion of electrons in the spectrometer’s CCD.
These emerald PL spectra (e.g., figure 3) exhibit local minima on either side of the R lines. To isolate the R-line contribution in each PL spectrum, a baseline is subtracted from the data. The line’s endpoints at 678.5 and 688.5 nm were selected to coincide with these local minima. The resulting spectra (e.g., figure 5) are referred to as R-line spectra.
The R-line spectra in figure 5 each show two lines with width and peak separation at least an order of magnitude larger than the spectrometer’s resolution. Besides the two peaks, no other fine structure appears in the spectra. After creating an R-line spectrum, peak-finding software (O’Haver, 2014) was used to extract R1 and R2 peak wavelengths and corresponding count rates, which were used to determine an R1/R2 peak height ratio. The R1 and R2 peak wavelengths reported here are means of values extracted from four separate spectral measurements. The resulting uncertainty in peak position is ±0.02 nm, as given by the four measurements’ standard deviation of the mean.
The first step in analyzing the R-line datasets was to examine how R-line peak wavelength distributions vary with sample origins. This is done by performing independent sample t tests on R-line peak wavelength values from samples with two different geographic origins (Crow et al., 1960). The Discussion section contains examples of how a random sample’s measured R-line wavelength can be compared with measured distributions to either support or reject possible origins.
We then determined whether a linear relation exists between R-line peak wavelengths and concentrations of a particular trace element by calculating the coefficient of determination r2 between the two datasets. In linear regression analysis of two variables, the coefficient of determination represents the fraction of variance of one dataset that is predictable from a “best-fit” linear relation with the other dataset (Crow et al., 1960). The coefficient of determination can range between 0 and 1, and two datasets are identified as strongly correlated when the coefficient of determination between them has a value r2 ≥ 0.64.
An issue arises from comparing R-line peak wavelengths extracted from the PL spectra to the trace element concentrations measured by LA-ICP-MS. In particular, the laser-illuminated volume in a sample that produces PL may not coincide with the surface spots where laser ablation was applied for mass spectrometry. This is a concern because trace element concentrations in natural emerald crystals can, and generally do, vary throughout the samples (Schmetzer, 1994; Schmetzer and Bernhardt, 1994). As a result, the LA-ICP-MS spot measurements of trace element concentrations may not perfectly match average concentrations within the bulk PL emission volume. This can reduce coefficients of determination between R-line parameters and trace element concentrations, leading to outliers in the resulting scatterplots.
In this report, scatterplots are presented for the R-line peak wavelength vs. trace element concentration datasets that demonstrate the highest coefficients of determination (i.e., strongest correlation). Next, linear regression is used to find each scatterplot’s “best-fit” trend line, where the slope of this line corresponds to the pairwise variation of the dataset, and where its intercept identifies the R-line’s peak wavelength for zero concentration of the trace element.
RESULTS
Examining R-line spectra extracted from the emeralds’ PL spectra (figure 5), we see that the Colombian sample’s R1 line peaks at the shortest wavelength, the Afghan sample’s line at a longer wavelength, and the Zambian sample’s line at the longest wavelength. A plot of the mean R1 peak wavelength of samples from each origin (figure 6) shows that this origin-based peak shift holds true on average. An overlap between Afghan and Colombian samples, seen in figure 6, results from a single anomalous R1 peak wavelength value in each origin’s dataset.
To compare R1 peak wavelength distributions between Colombian and Afghan samples, we performed an independent sample t test. The t test uses the following values from each geographic sample’s wavelength distribution: number of samples (N), mean wavelength value (M), and the standard deviation (SD) of these values. The t test produces a t value, t(df), where df represents the degrees of freedom. One then uses the t value to determine fractional probability (p) that the two populations share the same mean value, and to determine the 95% confidence interval (95% CI) for the difference between their mean values. The results show extremely significant differences in the distributions for the Colombian (N = 20, M = 683.777 nm, SD = 0.060 nm) and Afghan samples (N = 16, M = 684.013 nm, SD = 0.084 nm); t(34) = 9.88, p < 0.0001, and 95% CI [0.188 nm, 0.285 nm]. The low p value between this pair of sample datasets suggests that the measured difference between their mean peak wavelengths probably does not arise from an accident of sampling.
An independent sample t test was also performed between Afghan and Zambian samples. Similarly, there were extremely significant differences in the distributions for the Afghan (N = 16, M = 684.013 nm, SD = 0.084 nm) and Zambian samples (N = 12, M = 684.214 nm, SD = 0.046 nm); t(26) = 7.46, p < 0.0001, 95% CI [0.145 nm, 0.255 nm]. Once again, the low p value between this pair of sample datasets indicates that the measured difference between peak wavelengths probably does not arise from an accident of sampling.
Comparing the R1 peak wavelengths dataset with each trace element concentration dataset (table 1) provided by GIA, the Mg and Na concentration datasets have very strong correlations with the R1 peak wavelengths dataset. Each concentration dataset has the same coefficient of determination with the wavelengths dataset, namely r2 = 0.83. By contrast, comparisons between the R1 peak wavelengths dataset and all other trace element concentration datasets yield values for coefficients of determinations below 0.64.
A plot of all samples’ R1 peak wavelength vs. Mg concentration (figure 7) illustrates the first correlation. For this case, the best-fit trend line resulting from linear regression predicts a minimum R1 peak wavelength (with no Mg concentration) of 683.65 nm and a peak shift of 0.048 nm per 1000 ppma increase in Mg concentration. The scatterplot also outlines the trend line’s 95% confidence band, where a new data point collected from a random sample is predicted to fall within this band 19 times out of 20 (Natrella, 2013).
Very similar correlation is seen in a plot of all samples’ R1 peak wavelength vs. Na concentration (figure 8). The trend line here predicts nearly the same minimum R1 peak wavelength (with no Na concentration) of 683.66 nm and a peak shift of 0.041 nm per 1000 ppma increase in Na concentration. The scatterplot also shows this trend line’s 95% confidence band.
Returning to the R-line spectra (figure 5), the Colombian and Afghan samples’ R2 lines peak at similar wavelengths, while the Zambian sample’s line is shifted to a shorter wavelength. A plot of the mean R2 peak wavelength of samples from each origin (figure 9) shows that Colombian and Afghan samples’ mean peak positions are overlapped by the extreme values in their distributions. In contrast, the mean peak position of Zambian samples is shifted to a shorter wavelength and is not overlapped by the other samples’ distributions.
To compare R2 peak wavelength distributions between Afghan and Zambian samples, independent sample t tests were performed. The results show extremely significant differences in the distributions for the Afghan (N = 16, M = 680.699 nm, SD = 0.042 nm) and Zambian samples (N = 12, M = 680.461 nm, SD = 0.041 nm); t(26) = 15.00, p < 0.0001, 95% CI [0.205 nm, 0.270 nm]. Here, the p value for the Afghan and Zambian samples indicates little probability that they share the same mean value for R2 peak wavelength.
An independent sample t test was also performed between Colombian and Afghan samples. The results show no significant differences in the distributions for the Colombian (N = 20, M = 680.712 nm, SD = 0.047 nm) and Afghan samples (N = 16, M = 680.699 nm, SD = 0.042 nm); t(34) = 0.87, p = 0.39, 95% CI [0.017 nm, 0.044 nm]. This high p value for the Colombian and Afghan samples indicates significant probability that they may share the same mean value for R2 peak wavelength.
When the R2 peak wavelengths dataset is compared with each trace element concentration dataset, Li ion concentration (table 1) has the strongest correlation, with coefficient of determination r2 = 0.79. The Na ion concentration dataset also shows strong correlation with R2 peak wavelengths, with coefficient of determination r2 = 0.68. The coefficients of determination between the R2 peak wavelengths dataset and all other trace element concentration datasets have values well below 0.64. A plot of R2 peak wavelength vs. Li concentration (figure 10) illustrates their correlation. Here the best-fit trend line predicts a maximum R2 peak wavelength (with no Li concentration) of 680.74 nm and a peak shift of –0.154 nm per 1000 ppma increase in Li concentration. The scatterplot also shows this trend line’s 95% confidence band.
Examining the full set of PL emission spectra (again, see figure 3), it is apparent that even though the narrow R lines’ structure varies from one location to another, the overall shape of the broadband structure is roughly similar. As the PL emission arises from Cr substituting at Al sites in the beryl crystal, we first consider if the peak count rate of this broadband structure (located at about 715 nm) might be directly proportional to the emerald sample’s Cr concentration. A plot of all samples’ broadband peak count rates vs. Cr concentration (figure 11) shows no evidence that they are directly proportional. In this plot, most Colombian samples have low Cr concentrations and high count rates. Then there were Zambian samples that had high Cr concentrations and very low count rates, and Afghan samples appear all over the plot. Granted, the peak count rate does also depend upon the PL collection efficiency of the instrument. But with the luminescence collection volume (defined by the overlap of light beam, emerald, and optical fiber field of view) confined along one edge of the emerald, and with an effort to position the emerald edge to maximize these count rates, we do not expect much variation in collection efficiency.
As mentioned earlier, Fe ions can also substitute at Al cation sites in the beryl crystal, and it is well known that Fe dissipates PL emission by Cr (Nassau, 1978). A plot of all samples’ broadband peak count rates vs. Fe concentration (figure 12) shows that count rates drop exponentially with increasing Fe concentration. Thus, the high Fe concentration in Zambian emeralds explains the low values of their observed count rates.
Following these examinations, we attempted to construct an empirical model where peak count rate was proportional to Cr concentration and decayed exponentially with increasing Fe concentration. In testing this model against our data, we found that peak count rate was better predicted when it was proportional to the square root of Cr concentration. The empirical formula we found that best predicts count rate I is
where [Cr] and [Fe] are chromium and iron atomic concentrations, respectively (see box B). The empirical parameter B in the exponent is the Fe concentration that reduces Cr photoluminescence count rate by a factor of ten, while the parameter A represents the instrument’s collection efficiency. Rewriting equation 1 as a linear function of iron concentration [Fe]
suggests plotting the common logarithm of each sample’s ratio vs. iron concentration (figure 13). This pair of datasets has a coefficient of determination r2 = 0.85. Linear regression establishes values for the empirical parameters. The best-fit value for A is 1400, but this parameter is not much use beyond our experiment since it would have to be refitted for a different setup. The best-fit value for B is 2200 ppma Fe. This B parameter is independent of experimental setup, and it quantifies the low count rates observed from Zambian samples. In figure 13, all Zambian samples have Fe concentrations above the 2200 ppma concentration, reducing PL emission by a factor of ten; several samples have Fe concentrations above 3300 ppma concentration, reducing emission by a factor of 30. With the empirical parameters determined from regression, the empirical formula predicts count rates in our setup within a factor of two of all samples’ observed count rates except for two Afghan samples. The formula underestimates count rates of these two samples by about a factor of six.
DISCUSSION
Using an R-line Wavelength Measurement to Reject a Possible Origin. R-line peak wavelength values extracted from the PL spectra of emeralds exhibit distributions that tend to be localized according to geographic origin. Here we consider how one might use these distributions as an aid to origin identification. Assuming each origin’s measured distribution of R-line peak wavelengths represents that population’s true normal probability distribution2, we consider an R-line peak wavelength extracted from a random sample’s PL spectrum. If the random sample’s origin is completely unknown, and its origin might not be any of the three considered here, how can knowledge of the sample’s R-line peak wavelength be used to reject one or more of these as possible origin assignments?
Answering this question requires setting a significance threshold. If a comparison of the sample’s R-line measurement with an origin population’s distribution has a p value that is less than the chosen significance threshold, then that population is rejected as a possible sample origin. Here the p value is the probability of measuring an R-line peak wavelength from a population’s sample that is equal to or more extreme than what was actually measured (Kahn, 2016). Given the uncertainties in the mean values and standard deviations of distributions presented here, one might choose to set the significance threshold at an extreme value of 0.0001.
The rejection criterion can be simplified by using a z score. The z score between a measured value x and a population with mean M and standard deviation SD is given by z = |x – M|/SD, and it identifies how many standard deviations away from the mean the value x falls (Natrella, 2013). The range of probability values p < 0.0001 corresponds to a z score range of values z > 3.70 (Abramowitz and Stegun, 1972). If the z score between a random sample’s R-line peak wavelength measurement and an origin population’s peak wavelength distribution is greater than 3.70, then that population is rejected as a possible sample origin.
As an example, consider an extreme R1 peak wavelength value that appeared in our Colombian dataset. The R1 peak wavelengths of most Colombian samples cluster around the reported mean value M = 683.777 nm with standard deviation SD = 0.060 nm. But as shown in figures 7 and 8, one sample known to be of Colombian origin has an R1 peak wavelength value x = 683.946 nm. Of the 20 Colombian samples reported here and six other examples reported by Thompson et al. (2014), this value is by far the most extreme recorded for a Colombian sample. The z score between this sample’s R1 peak wavelength and the Colombian distribution is z = 2.817, so it does not meet the threshold for rejection.
However, the z score between that sample’s R1 peak wavelength and the Afghan distribution is only z = 0.798, well below the rejection criterion. If the origin of this sample was truly unknown, we could not reject either Colombia or Afghanistan. In contrast, the z score between the sample’s R1 peak wavelength and the Zambian distribution is z = 5.826, which exceeds the threshold for rejection. Therefore, Zambia can be rejected as a possible origin.
As another example, could a sample with R1 peak wavelength equal to x = 684.000 nm possibly be from Colombia? The z score between this R1 peak wavelength and the Colombian distribution is z = 3.717, which exceeds the minimum z value for rejection. We therefore would reject Colombia as a possible origin for any sample with R1 peak value at or above this wavelength.
Identifying a Mechanism Responsible for Shifts in R1-Line Peak Wavelengths. We propose that the trace element dataset producing the highest coefficient of determination with a particular R-line dataset is most likely the impurity substitution responsible for shifting the R-line’s peak wavelength. When two or more trace element datasets produce similar high values of r2 with the R-line’s dataset, we must consider how each may be involved with the R-line’s peak shift.
As noted earlier, the shift in R1 peak wavelength with increasing Mg and Na impurity concentrations shows very strong correlations, with the same coefficient of determination for both concentration datasets, r2 = 0.83. These strong correlations suggest that the R1 peak shift arises primarily from the aliovalent substitution of Mg at Al octahedral crystal sites, with charge balance provided by Na occupying an open channel site: Al3+ ↔ Mg2+ + Na+.
Comparing the Mg and Na ion concentration datasets reveals that the presence of one ion correlates very strongly with the presence of the other, with a coefficient of determination r2 = 0.99 between the two datasets. Yet a plot of Mg vs. Na concentration (figure 14) does not exhibit a one-to-one match, where each Mg ion would be accompanied by exactly one Na ion. In fact, the trend line resulting from linear regression reveals a slight excess of Na ions, where 10 Mg ions are matched by 11 Na ions. This 10% difference between Na and Mg ion concentrations may arise from a matrix effect in the LA-ICP-MS measurements (Sylvester, 2008). The efficiency with which different ions are ablated from the NIST glass matrix used for calibration may differ slightly from the efficiency of ions released by ablation from beryl matrix. If an excess of Na ions does not originate from a matrix effect, however, these ions may contribute to the R2 peak shift, as described below.
Identifying a Mechanism Responsible for Shifts in R2-Line Peak Wavelengths. As noted in the Results section, the R2 peak wavelengths dataset exhibits strong correlation with the Li ion concentration dataset, with coefficient of determination r2 = 0.79. The lack of correlation between R2 peak positions and divalent and trivalent cation concentrations suggests that substitution at Al crystal sites is not responsible for the R2 peak shift. Conversely, Li is the only cation that substitutes at the tetrahedral Be crystal site in beryl (Aurisicchio et al., 1988). To maintain charge balance, an accompanying alkali ion also must occupy an interstitial site. Besides Li concentrations, only the Na concentration dataset shows any significant correlation with the R2 peak wavelengths dataset, with coefficient of determination r2 = 0.68.
As described above, most Na atoms appear to be paired with Mg atoms. In attempting to isolate the “excess Na” concentration (comprised of those Na ions not paired with Mg) by subtracting Mg concentrations from corresponding Na concentrations, the resulting excess Na concentration dataset shows slightly stronger correlation with R2 peak positions than does the full Na dataset, with coefficient of determination r2 = 0.72. Adding the excess Na concentrations to corresponding Li concentrations creates even stronger correlation with R2 peak positions, with coefficient of determination r2 = 0.83. This coefficient of determination is higher than that achieved using the Li dataset by itself.
Comparing the Li and excess Na ion concentration datasets gives a coefficient of determination r2 = 0.66, just barely exceeding the strong correlation threshold. A scatterplot of Li concentrations vs. excess Na concentration (figure 15), along with a best-fit trend line, demonstrates the correlation. The scatterplot does exhibit many outliers, including examples where subtracting a sample’s Mg concentration from the corresponding Na concentration produces a slightly negative value. Overall, there appear to be several instances where there is not enough excess Na to match up with Li.
The strong correlation between samples’ R2 peak wavelengths and Li impurity concentrations suggests that the R2 peak shift arises primarily from Li ions substituting at the tetragonal Be crystal sites. Interpreting correlations of excess Na impurity concentrations with the R2 peak shift and with Li concentrations suggests that when Na ions are available, they may provide charge balance for the substitution. When Na ions are not available, we propose that the charge balance may be maintained by an additional Li ion occupying an open channel site: Be2+ ↔ Li+ + Na+, Li+.
CONCLUSIONS
We have collected photoluminescence spectra of emerald samples from Colombia, Afghanistan, and Zambia. Extracting peak wavelengths of R lines appearing in emerald’s E⊥c PL spectrum, we observed that values tend to be distributed according to geographic origin. With knowledge of localized distributions from a given origin, an R-line measurement of a random sample can provide evidence for or against the possibility of that origin.
Emerald samples from these three different origins were selected because they displayed distinctly different trace element impurity concentrations. Comparing peak positions of their R lines with corresponding concentrations of impurity ions, we have identified strong correlations between R-line peak shifts and increasing concentrations of specific impurities. In particular, the R-line peak wavelengths can also be used to estimate concentrations of three non-chromophore impurities in emerald: magnesium, sodium, and lithium. This assessment can supplement measurements of these impurities using other chemical composition analysis techniques, such as X-ray fluorescence, electron microprobe analysis, and LA-ICP-MS. The correlations also suggest likely mechanisms responsible for the R-line peak shifts.
Finally, comparing peak intensities of the broadband structure appearing in PL spectra with corresponding concentrations of chromium and iron impurities led to identification of an empirical formula where photoluminescence count rate increases with the square root of chromium concentration and decreases exponentially with increasing iron concentration. While it has long been known that iron impurities tend to quench chromium photoluminescence in gemstones, here we have quantified this effect.