1. Introduction
The studies of tree rings have been a powerful instrument in environmental research due to the tree rings’ ability to provide annual resolution of data and long data sequences. While the tree ring width as well as the cell morphology and wood density served to be primary parameters of the rings in dendrochronology, since the 1970s–1980s, studies of element concentration in trees have been developing by the area of environmental chemistry. A combination of tree ring analysis and elemental analysis have given a new perspective to environmental research [
1].
Due to obvious practical importance, the dendrochemical tree ring studies have often concentrated on the emissions of pollutants as a result of industrial activities [
2,
3,
4,
5,
6,
7,
8]. This area of inquiry has a clear significance for the practice of legal actions against subjects committing pollution.
Another developing research area deals with relationships of elemental content in tree rings and the factors of physical environment, which includes events from ancient volcano eruptions to actual weather conditions. Hevia et al. [
9] have found that a number of elements peaked around the years of known eruptions in tree rings in Pyrenean Mountain pine. Also, the authors related the elemental variations to temperature and precipitation factors. Sometimes, to reveal the relations with weather parameters, one needs to subject the wood samples to additional treatment. Scharnweber et al. [
10] suggested to extract the wooden specimen in a number of solvents (water, alcohol, and acetone) to separate the elements tightly bound in wood from volatile substances inducing noise into the environmental signal. Gavrikov et al. [
11] used some other chemical agents (alcohol and hydrochloric acid) and found that only after the treatment were correlations of elemental content with meteorological parameters able to be found in some species (esp., in Siberian larch).
A complication—worthy of attention for both practical and theoretical research—is that sufficient variations of inorganics’ content are observed among and within species [
12]. Thus, this variety may obscure the relationships sought. A question has been inspected whether the elemental sequences obtained from different sides of the same Scots pine tree correlate with each other [
13]. The inference was that the sequences of the majority of expected elements in sequences from different trunk sides did not correlate, with a couple of exclusions which are Ca and K having long trends across tree trunks. Consequently, an apparent lack of consistency may affect the reliability of a research outcome.
It is well known since long ago that the growth of tree rings pursues a definite seasonal pattern in temperate tree species. Typically, the sequences of cells in a tree ring are subdivided into early-wood, with larger lumens and thinner cell walls, and late-wood, with narrower lumens and thicker cell walls. Such a pattern, despite the differences in wood structure, is characteristic of both conifers and dicots among trees [
14,
15,
16]. However, as Vaganov et al. [
1] pointed out, the intrinsic factors leading to different rates and durations of the tracheid formation and their specific morphology remain poorly understood. Not only are physical wood properties different within a single tree ring but the early- and late-wood also bear biochemical and chemical differences.
For example, the late-wood in Norway spruce contained significantly more galactomannan and less pectins than the early-wood [
17]. In the same species, the relative-to-cellulose content of lignin is significantly higher in the early-wood which was shown with the help of Raman microspectroscopy and infrared spectroscopy [
18]. The early-wood vessels were rich in guaiacyl lignin while the vessels of late-wood were rich in syringyl lignin in English oak [
19]. Antonova et al. [
20] have shown that syringyl and p-hydroxiphenil aromatic residues prevailed in the course of early xylem maturing in Scots pine. At the same time, the maturing xylem of the late-wood contained an increased share of guaiacyl residues.
Regarding the inorganics, the studies of early- and late-wood are rather scarce. Hevia et al. [
9] reported on differences in elemental contents between early-wood and late-wood in Mountain pine, including especially how Ca was found to peak in the early-wood after which Ca was decreasing closer to the late-wood.
Our experience shows that a lack of consistency in the chemical effects found in tree rings may be a serious obstacle for progress in this research area. The effects may be obvious in one sample/tree and absent in other samples/trees. Thus, the primary purpose in the field should be the establishment of relationships between elements and the anatomical structures of wood as well as among the elements residing in the xylem.
The goals of this research were as follows: (a) to find, among a number of elements, relationships between early- and late-wood which were consistent enough within tree and among trees; and (b) to find consistent correlations between elemental content in early- and late-wood, on the one hand, and available meteorological parameters, on the other hand.
2. Materials and Methods
2.1. Geographical Location and Species
For this study, an even-aged Scots pine (
Pinus sylvestris L.) stand was taken. The trees were planted as 2–3-year-old seedlings in 1971–1972 as a part of an afforestation experiment with an initial planting density of 40,000 saplings per ha [
21,
22]. The location of the experiment area is shown in
Figure 1.
2.2. Sampling
In autumn 2021, six apparently healthy pines of ca. average size were randomly chosen for the sampling. From each tree, two 12 mm cores were extracted at breast height with the help of a Haglöf borer (Haglöf Sweden AB, Långsele, Sweden), with one from the southern and one from the northern sides of the tree stem. Altogether, 12 cores were sampled and further treated. Under room conditions, the cores were air-dried in a laboratory. With the help of a circular saw, 1.2 mm thick slices were made from the cores perpendicular to the wood grain. The sampling and the subsequent treatment of the cores were performed in observance of basic approaches accepted in dendrochronology [
23].
2.3. X-ray Scanning
X-ray facility Itrax Multiscanner (COX Analytical Systems AB, Mölndal, Sweden, 2012) coupled with Multi Scanner Navigator software 6.5.3. was used to scan the slices.
Itrax Multi Scanner excites the elements’ nuclei by a thin X-ray 20 mm by 50 µm beam and detects the energy of the responsive radiation. The radiation is registered by a Si-based detector SDD (Ketek GmbH, München, Germany). The resolution of the detector is 140 eV at 5.9 keV and it can register up to 200,000 photons a second (cps). The spatial resolution of scanning was 100 µm. The analysis of light elements at an acceptable detection limit is performed through an X-ray tube with a Cr anode (1.9 kWt). For Ti and heavier elements, an X-ray tube with Mo anode (3 kWt) is used.
Altogether, the chemical elements monitored in the research included Al, Si, P, S, Cl, K, Ca, Ti, Mn, Fe, Cu, Zn, Sr, and Hg. The reason to choose the elements was that most of the elements are either biologically active or may be biologically active. Also, a parameter physically describing the wood specimen was included which is the registered incoherent radiation, denoted as ‘inc’ in the subsequent tables.
For each element and for each scanning point, the multi-scanner produces a long series of data which are relative units (counts per second). The counts are theoretically related to the number of the element nuclei contained in the point of scanning.
In addition to the counts data, Itrax Multiscanner outputs X-ray images of the wood specimen allowing for sure recognition and dating of the tree rings.
2.4. Time Span of Data
An important detail is the time span included into the analysis. Because of the goals of the research, the widths of both early- and late-wood were crucial for the analysis. Still, the majority of outer tree rings are rather narrow, and so often a single, if any, scanning point falls within the late-wood thus making the measurements unrepresentative. At the same time, the studied rings should not be at the very pith.
The last growth year was 2021 but only a row of tree rings that are wide enough were taken for the analysis. They are 11 years, from 1981 to 1991. An example image depicting the growth rings under study is shown in
Figure 2.
2.5. Meteorological Data
The meteorological dataset has been used in a previous study [
11]. The initial source of the data is the database of the Krasnoyarsk Weather Station, WMO ID = 29570.
Twenty-one various weather parameters were used in the study: (1) mean monthly humidity (from May to August), (2) mean monthly temperature (from May to August), (3) monthly sum of precipitations (from June to August), (4) mean monthly wind speed (from May to August), and (5) a compound humidity index by Vysotskii–Ivanov (from June to August). The latter index has been represented in two forms, ‘as is’ and detrended, and thus is in the form of indices.
The humidity index (
HI) is calculated as
where
Pr denotes the monthly precipitation while
Ep denotes the monthly evaporation.
The precipitation data for May has not been used because the month is transient between winter and summer, and the precipitations may be in solid form.
2.6. Statistical Treatment
The early- and late-wood within a ring were visually separated on the X-ray images (e.g., as shown in
Figure 2). The scanning point closest to the outer border of late-wood stripe was considered to be the end of the ring. The scanning point closest to the inner border of the late-wood stripe was considered to be the end of the early-wood.
Because all the tree rings differ in width a different number of scanning points falls within the early- and late-wood of the rings. To eliminate the impact of the ring width, mean count rates per a scanning point were used throughout the analysis below. That is, for each core and each element, the mean count rates per a scanning point in the early- and late-wood were calculated. Alternatively, for another part of the analysis, the mean count rates were calculated per a scanning point within each tree ring, for the early- and late-wood in that ring combined.
According to the goals of the research, two main statistical methods have been applied. First, this is the standard comparison of means. Because the number of scanning points in the late-wood were 40–80 depending on the tree, the non-parametrical Mann–Whitney
U-test has been applied to compare the elements’ count rates in early-wood vs. late-wood. The non-parametrical approach allows one to avoid dealing with normality tests. All the early-wood data of a tree were compared to all the late-wood data of the same tree. Then, the results of all the trees were compared against each other. Second, possible relationships between the elements’ contents and the weather parameters have been estimated through a classical correlation analysis. Due to the small number of data points, a non-parametrical Spearman’s rank correlation has been applied. All the calculations have been performed with the help of R statistical tools [
24].
4. Discussion
Similar to other scientific areas, the tree ring research is crucially dependent on the consistency factor. Controversial variations of measured values convert an anticipated relationship into a hardly explicable stochastic pattern. It has been found, for example, that there is a lack of correlations of elemental tree ring series among different sides of the tree trunk [
13].
Dendrochronology—which has been based on relations between climatic factors and the tree ring width—finds a way out by averaging a large number of tree ring series and obtaining a population response. Another approach may be to collect relationships that are significant in all available specimen, and then to formulate a research program that is founded on this firm basis.
The anatomy of a temperate tree ring has been known since long ago. It typically consists of early- and late-wood stripes the organic chemistry of which has been recently explored from many respects [
17,
18,
19,
20]. Regarding the inorganics in early- vs. late-wood, there is still a lack of consistent evidence. Hevia et al. [
9] have enumerated a number of results for Ca content in some conifers. Calcium mean content is higher in early-wood in Mountain pine, Siberian spruce, and Siberian fir, and inversely, Ca mean content is higher in late-wood vs. early-wood in bristlecone pine.
In this research, it has been found that, in addition to Ca, a number of important biophile elements may also show a consistent pattern between early- and late-wood. The core of the group is comprised by Cu, Zn, and Sr which always follow the same pattern in both tree trunk directions (North and South), and the differences between early- and late-wood are always significant. Phosphorus, calcium, and iron can also be considered as belonging to the group, although despite that their differences are always significant only in the northern trunk side but not in the southern one (
Table 1 and
Table 2). As follows from the ‘Time span of data’ subsection, the correlations were calculated with a limited number of data totaling 11 points. As the statistical significance is strongly dependent on the amount of data, the lack of significance may be related to the limited data. A larger amount of data (if they are available) may improve the problem of significance.
Like dendrochronology, dendrochemistry does not deal with alive cells but rather cells where the lumens are empty. Thus, the only place for the chemical elements to reside is the cell walls. It is well known that after cell death the cell walls remain rich in compound organic substances, such as lignins, pectins, pentosans, and others. All the organic molecules may contain active centers (like carboxyl groups –COOH or similar structures) which are able to exchange protons to metal ions flowing with the sap.
Because the organic speciation of early- and late-wood is to some extent dissimilar, diverse ions may be consistently attached to organic molecules in the alternative parts of the tree ring. Two elements, Cu and Zn, show a similar pattern, a persistent higher content in the late-wood vs. early-wood. The origin of such a behavior may be related to their atomic properties, that is, to the fact that the ionic radii of the elements are rather proximate. The ion Cu2+ has the radius 0.073 nm while Zn2+ has the radius 0.074 nm. Hypothetically, the elements may attach to active organic centers of the same kind which are more abundant in the late-wood.
Another remarkable pair of elements are Ca and Sr. They are considered to be geochemical analogs of each other because Sr often replaces Ca in minerals as well as in living tissues. The ion Ca
2+ has the radius 0.1 nm while Sr
2+ has the radius 0.118 nm which is somewhat larger but more or less close to the former to provide similar properties. Calcium variates consistently between early- and late-wood (
Figure 3) growing in the very beginning of the growth season and falling around the start of late-wood formation. This type of behavior has been found in a number of studies [
25,
26].
The Ca content decrease in the late-wood is moderate. However, Sr drops radically in the late-wood (
Figure 3), often down to “zero” values, which is probably the source of its steady significant difference between early- and late-wood. Because we deal with a facility that has its own technical limits of radiation detection, “zero” values are not obligatory real physical zero but a level that the facility percepts as the element absence.
Chemically, the absence may hypothetically mean that either Sr2+ loses out in a competition for active centers to Ca2+ or that Sr2+ just cannot attach to the active centers available in late-wood which may be due to a somewhat larger ionic radius.
The third opportunity is that Sr2+ is outcompeted by some other elements which are close to it in terms of ionic radii. A group of elements have ionic radii larger than Ca2+ but smaller than Sr2+. This group includes Ce3+ (0.101 nm), U3+ and Hg2+ (both 0.102 nm), and La3+ and Bi3+ (both 0.103 nm). However, all these elements are really very scarce in the mineral soil of the site. A preliminary estimation of the elements availability through ICP-AES (OES) atomic/optic emission spectroscopy (unpublished data) has shown that U and Hg are below the detection limit of the method, Bi is contained at 7.2, and Ce and La are contained at 53 and 32 mg/kg, correspondingly. To compare, Ca is found at 9864 and Sr is found at 166 mg/kg. Thus, it is unlikely that the group of scarce elements could influence the variations of Sr in the tree rings.
To summarize the differences in elemental contents in early- and late-wood, the consistent relationships may be a basis for an in-depth inquiry regarding why the elements are distributed in the wood this or that way. It is most probable that methods including extraction and re-scanning techniques [
10,
11] may help to penetrate into mechanisms of elemental sorption and distribution in tree rings.
Hevia et al. [
9] reported on elemental peaks of Ca, Fe, and some other elements’ content in tree rings in the years following known large volcanic eruptions. The eruptions led to abrupt summer cooling in many global areas and, probably, impacted the absorption and the distribution of elements within tree rings. However, well-described inner mechanisms through which such elemental reactions appear are not yet known.
Nevertheless, if some definite relationships steadily replicate within and among trees, then these relationships may be used to do a next step in research. In this study, the pairs ‘early-wood Ca–June humidity’, ‘early-wood Ca–June temperature’, and ‘late-wood K–June humidity index’ showed a rather consistent pattern in the sense that Spearman’s coefficients were high enough for all the sampled trees. Although the p-values are somewhat higher than that accepted in natural sciences, this may be in part attributed to low data availability. There is a hope that the significance levels may increase with a longer series of wide tree rings.
It is worth paying attention to how the correlation of early-wood Ca with June humidity is negative while its correlation with June temperature is positive (
Table 3 and
Table 4). Generally, high air humidity should suppress transpiration in plants, especially at the time of active growth. If so, then the amount of sap flowing through the tree trunk and carrying the ions should be lower. On the other hand, higher temperatures should lead to increased transpiration and more sap flowing through the tree trunk. If, hypothetically, the amount of deposited Ca is dependent on the amount of sap that has flown through the xylem, then these environmental factors may explain the Ca variations in tree rings.
A note should be made that the positive relation of Ca content to the ambient air temperature seems to contradict to some extent the observations of the Ca peaks after volcanic eruptions [
9]. A cooling in the environment should reduce the Ca content (
Table 4). However, the results presented here apply (1) only to June mean temperature and (2) to the normal weather conditions without excessive variations. Abrupt cooling for a longer time may be out of normal tree reactions and employ some different mechanisms of elemental distribution in the xylem.