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Springs with active precipitation in the Polish part of the Tatra Mountains

Agata Smieja 1, Beata Smieja-Król 2 1W. Szafer Institute of Botany, Polish Academy of Sciences, e-mail: [email protected] 2 Faculty of Earth Sciences, University of Silesia, e-mail: [email protected]

ABSTRACT During the field work carried out in the years 2002-2006 over the floral composition in 340 water-springs in the Tatra National Park (TNP) eight springs with calcium carbonate precipitation were detected. Eight springs drain water away from carbonate rocks in three areas generally: Kopieniec slope of Olczyska Valley, lower parts of Lejowa Valley and in Ko ścieliska Valley. Two types of spring CaCO 3 accumulation were identified relatively to intensity of the process and stability of the precipitation products. The calcifying 2+ – springs represent the highest Ca , and HCO 3 ions concentrations among all investigated springs. In comparison with typical tufa depositing springs, the values appear to be rather low.

KEY WORDS : carbonate precipitation, spring, the Polish Tatra Montains, tufa

Introduction

Calcareous tufas are, apart from accumulated as a fan at the foot of a rock wall. , the main sediments resulting In this site the precipitation ceased probably from decalcification of karstic water. Porous soon after the 13 – 14 century AD climatic tufa deposits form at or near the groundwater optimum (Alexandowicz, 1988). Another type outflow via the overall reaction: of freshwater calcium carbonate accumulations found in the Tatra Mts comprise slope breccias Ca 2+ + 2HCO - → CaCO ↓ + H O + CO ↑ 3 3 2 2 formed in Holocene or in the warm phases of Intensity of carbonate precipitation and Pleistocene. They are composed of locally deposition reveals close relationship with the derived carbonate rock fragments bound with local environment, and depends especially on cement. The calcite cement forms a humidity and temperature conditions laminated crust on the rock clasts (Kota ński (Andrews, 2006). The optimal climatic 1958; Gradzi ński et al. , 2001). Their formation conditions for tufa deposition in the Carpathian in recent times is limited probably to one Mountains and its foreland prevailed during occurrence recorded by Kota ński (1971). Holocene Atlantic Phase when due to intense Recent tufa-forming springs are denudation significant amount of calcium rare in the Polish Tatra Mts, although actively carbonate was released (Pulina, 1974). A forming tufa deposits are known from many decline of active tufa formation has been sites in Southern Poland (Mastella, 2001; observed in all Europe over the last three Alexandrowicz, 2004). Alexandowicz (1988) thousand years, probably due to the climatic suggested that the present climatic conditions change (Goudie et al., 1993). prevailing in the Tatra Mts are too severe for In the Polish Tatra Mountains fossil tufa tufa accumulation. As to our knowledge, the from the Kraków Gorge was described, where only known springs actively accumulating plants encrustated by calcium carbonate calcite, were described in Lejowa Valley 220 Agata Smieja, Beata Smieja-Król

(Głazek, 1965). Głazek (1965) found thin kode: 7220) are priority habitat types calcareous layers on rubbles, rocks and designated by European Union as particularly irregular oncolites of algae origin in three deserving intensive conservation care (Council small springs situated on the western slope of Directive 92/43/EEC). Their value is also this Valley. Another tufa forming spring accented in the Polish list of natural habitats located in the northern part of the Tatra Mts coming under protection (Dz.U. Nr 92, poz, was reported from Bobrowiecka Valley in 1029). Slovakia and was characterized by relatively In this work we present sites of active high temperatures of 14-16 ºC (Kowalski, precipitation of CaCO 3 found in the Tatra 1920). National Park (TNP) during a field work From the ecological point of view the carried out over vegetation in spring areas in calcareous crenal habitats with active calcium the years 2002-2006. A spring area is defined carbonate precipitation are very rare and here as a special habitat in and around the vulnerable phenomena with numerous rare and place where the groundwater comes to the endangered taxa (Wołejko 2004). “Petrifying surface, which is developed directly under the springs with tufa formation” (Natura 2000 water influence.

Methods

The water temperature and pH were atomic absorption spectroscopy (SOLAAR measured for each site in situ. Water was M6). Alkalinity was determined by titration. collected for laboratory measurements in Saturation indices (log IAP/K eq ) of the water selected springs in May and October 2006 and were calculated using a computer program, analyzed within three days of sampling. PHREEQC (Parkhurst, 1995). Calcium and magnesium were analyzed by

Results and discussion

Site description 340 spring areas were investigated in relation to floral composition as a main topic of the study carried out during the four years. 240 of the studied springs emerge from carbonate rocks. Calcium carbonate precipitates were detected in eight springs (Fig. 1) which drain away water from carbonate rocks generally in three areas: Kopieniec slopes in Olczyska Valley (Dolina Olczyska), lower parts of Lejowa Valley (Dolina Lejowa) and in Fig. 1. Localization of investigated springs in the Tatra Ko ścieliska Valley (Dolina Ko ścieliska), all National Park. I - sedimentary rocks (mainly carbonates), located within the lowest climatic-vegetation II - crystalline rocks, III - Pleistocene deposits (mainly zone (lower montane belt). The calcifying moraines), IV - Podhale flysch, V – state border, VI - the springs can be roughly divided into two types TNP boundary. Springs with active calcium carbonate precipitation in the Polish part of the Tatra Mts. 221 relating to intensity of the process and stability of the precipitation products.

Table 1. Synthesis of the most important ecological features of carbonate precipitating springs

Vegetation Water Spring Spring Altitude Slope cover in the Geological * Locality Coordinates temp. discharge o area (m a.s.l.) ( ) spring area basement (oC) (l/s) (m 2) (%) Lejowa N49 16 10.7 1 990 6.1 0.1-1 35 128 94 Valley E19 50 30.6 Lejowa N49 15 49.9 2 1120 6.3 0.1-1 40 11 53 limestone Valley E19 50 12.0 Lejowa N49 15 32.6 3 1110 5.3 0.1-1 35 107 70 shale Valley E19 50 30.4 Staników N49 16 00.5 4 1210 8 0.1-1 10 94 90 limestone Gully E19 53 00.4 Mi ętusia N49 15 50.1 5 1185 9.4 0.1-1 25 27 50 limestone Valley, E19 52 51.2 Ko ścielis N49 15 20.7 clay, 6 ka 1124 5.2 0.1-10 30 56 62 E19 52 37.5 limestone Valley Olczyska N49 16 27.2 7 980 7.5 0.1-1 70 33 48 limestone Valley E20 00 04.5 Olczyska N49 16 31.3 clay, 8 1080 9 0-0.1 30 15 79 Valley E20 00 25.6 limestone * - numbers in the table correspond with numbers used in the map

The first type is represented by two springs meters above the level of the Olczyski Stream with evidently long term accumulation of (Fig. 2). Discharge of water from the contact calcium carbonate. They detailed characteristic of a limestone and weathered rock ranges from are given below. The main ecological features 0.1 to 1 l/s. The upper part of the spring area is are summarized in Table 1. completely covered by dense carpet of moss

Fig. 2. A general view on an intensively calcifying spring Fig. 3. Intensive CaCO 3 precipitation of Palustriella in Olczyska Valley (no 7). commuta mats (spring no 7).

The first spring area is localized at the Palustriella commutata (species typical for bottom of Olczyska Valley on the right side of springs on carbonate bedrock). Because of the Olczyski Stream (number 7 in Table 1). It is high slope inclination in the lower part of the developed on a steep (about 70 o), rocky spring area, the bryophytes carpet is developed surface with the water emergence about seven to lesser extend and does not cover more than 222 Agata Smieja, Beata Smieja-Król

30 % of the spring area. The outflowing water together with small stones. Palustriella seeps slowly through the moss carpet and then commutata dominates in the upper part of the trickles down the rock. 5-10 cm thick porous area forming a dense carpet and higher plants moss-tufa deposit (Fig. 3) is forming under the like Festuca carpatica and Viola biflora moss which is growing upward while its lower inhabit the lower part. In the upper part, the parts become calcified. Due to the steep slope, calcite encrusted the lower, water soaked parts fist-size fragments of the highly porous moss- of the moss. The higher plants grow in tufa peel off and fall directly to the stream separate clusters within the lower part of the where they are washed away at higher water spring area and thin calcite crust develops levels, limiting tufa accumulation at this site. there not only on living plants but also on all The limestone bedrock is covered by a available surfaces present within the spring laminated tufa-crust up to 0.5 cm thick (Fig. 4) area like pebbles, dead leaves, twigs, etc. in the lower part of the spring area. Loose fragments of moss-tufa were also seen.

Fig. 4. Carbonate crust on limestone rock from the lower Fig. 6. Gothic arch calcite crystals on a moss branch part of the spring in Olczyska Valley (no 7). (spring no 8).

Fig. 5 . SEM photomicrograph of Palustriella commutata Fig. 7. Twinned calcite crystals on a moss leaf (spring encrusted by CaCO 3 (spring no 8). no 8).

Calcite precipitation of similar intensity as After about 10 meters the spring waters flow the one described above was detected within a down to a nearby periodic stream. spring area localized on Adamica slope in In the second, more often observed, type Ko ścieliska Valley (number 6). The substrate of springs the calcification is less intensive and of this site is unstable, composed of a loam was observed only on lower, water soaked Springs with active calcium carbonate precipitation in the Polish part of the Tatra Mts. 223 parts of bryophyte layer. The lower parts of the the mosses. Euhedral crystals of different mosses are tightly covered by a thin morphology were observed (Fig. 6, 7). Springs (maximum 1 mm) carbonate crust (Fig. 5) not of this group are very similar in seen on the surface of the moss carpets. Under ecomorphology. All are typical helocrenes SEM, the CaCO 3 consists of micritic and (seepage springs). sparry calcite crystals that grow directly upon

Table 2. Chemical analyses of water (average values from two measurements done in May and October) from selected springs. Ca 2+ Mg 2+ HCO - * Locality pH 3 SI (mg/l) (mg/l) (mg/l) calcite 1 Lejowa Valley 8.3 62.69 4.16 180.01 0.72 4 Staników Gully 7.8 80.00 12.16 311.30 0.57 6 Ko ścieliska Valley 7.72 61.80 1.78 186.87 0.15 7 Olczyska Valley 7.6 54.47 14.05 218.37 0.08 * - numbers in the table correspond with numbers used in the map

A good example of this type of springs is provided by a spring area located on the left side of Lejowy Stream near the entrance to the Factors controlling calcium carbonate valley (number 1). This site is irrigated along precipitation the whole spring area and it represents a non- The concentrations of Ca 2+ , Mg 2+ and – concentrated source of groundwater. The HCO 3 ions in the calcite precipitating springs substrate is composed of limestone pebbles are among the highest values when taking into and flattened boulders. Water in the upper part account all springs in the Tatra Mts, for which is invisible on the surface and slowly seeps the data were available (Fig. 8). Other ions are through dense moss carpets appearing at the present in very low concentrations. Ion end of the spring area, where it forms small concentrations in the springs are relatively trickles. The whole spring area is covered by stable over time (Oleksynowa, Komornicki, moss layer predominated by Palustriella 1996). commutata. Other species of bryophyte, e.g. Bryum pseudotriquetrum and Philonotis calcarea are also present , but in much lower abundance. In the herb layer Petasites albus , Viola biflora and Heliosperma qudridentatum were noted. A different situation occurs in the spring area (number 4) in Staników Gully. The water emerges on a weak inclination slope and forms a small stream. On its both sites a swampy zone with the same vegetation composition as in the helocrene described above has developed. There are only small tufts of P. commutata growing directly in the 2+ 2+ - Fig. 8. Ca , Mg , HCO 3 concentrations in springs on stream . A weak calcite encrustation is visible carbonate substrate ( □,■- data compiled from only on the bedrock and on the mosses tufts Oleksynowa, Komornicki, 1956, 1957, 1958, 1960, 1964, along the main stream. 1989, 1990 and ○,● - authors’ data)

224 Agata Smieja, Beata Smieja-Król

Although the calcite precipitating springs (Table 1) and a moss cover which is represent the highest ion concentrations within particularly dense immediately to the water the Tatra Mts, when compared with typical emergence. The dense carpet of bryophyte tufa depositing springs, the values appear to be slows down the water flow and serves as a rather low. Hajek et al. (2002) found the nucleation site for the carbonates. Apart from minimum calcium concentration needed for the passive control of mosses on carbonate occasional calcite precipitation to be about 90 precipitation, induction of supersaturation by mg/l and for forming reinforcement tufa photosynthetic uptake of CO 2 and water deposits to be about 250 mg/l in spring fens in evaporation can play an important role in this the Western Flysch Carpathians. In the environment. It should be noted however that investigated springs the highest calcium mosses are not generally considered to play an concentration was found in water emerging active role in the carbonate precipitation as in from Staników Gully (no 4) and it was 80 mg/l the case of cyanobacteria and algae (Merz- (Tab. 2). The calcium concentration in the two Prei β, Riding, 1999). Pentecost (1980) visually most intensively calcifying springs attributed the encrustation of Palustriella (no 6, 7) was 50-60 mg/l and the values are commutata to the presence of epiphytic distinctly below the value estimated by Hajek cyanobacteria which trap calcite particles. Our et al. (2002) for the ephemeral calcite SEM investigations do not confirm any precipitation (90 mg/l Ca). significant moss colonization by micro- The basic condition for calcite organisms; the calcite is deposited directly on precipitation is that the solution becomes moss tissues but without preference of any supersaturated, i.e. that saturation index (SI) particular moss part (Fig. 6, 7). exceeds zero. Results of chemical modeling The case of the spring in the Staników using PHREEQC (Parkhurst, 1995) show that Gully is consistent with the observations all the described springs are slightly conducted by Hajek et al. (2002). The calcium supersaturated with respect to calcite, with the concentration in the Staników spring waters is SI value being within the range of 0.08 – 0.72 near the value needed for occasional calcite SI (Table 2). However it is a well known precipitation and therefore the observed weak phenomenon that kinetic constraints permit encrustation of the spring bed resulted substantial supersaturation to occur without probably directly from water chemistry at this resulting in calcite precipitation (House, 1984). site. Calcium carbonate precipitation in streams More research is needed to explain the becomes conspicuous when average annual SI mechanism of calcite precipitation in the Tatra values exceed 0.75, and significant tufa springs and to evaluate the role of bryophytes deposition occurs above SI 0.85 (Merz-Prei β, in the process. As pointed out by Janssen et al. Riding, 1999). Lower calcium concentrations (1999) active tufas can be regarded as natural and SI values between -0.1 and 0.5 were also laboratories where carbonate precipitation can noted in sites with calcite precipitation (Boyer, be studied in situ and because they are always Wheeler, 1989). associated with micro-organisms and higher The visual inspection of the springs in plants, these sites form suitable research relation to the water chemistry leads to the objects for answering the question about the conclusion that the ions saturation is not a possible biological influence on carbonate definitive factor controlling the calcite precipitation. The presented tufas from the precipitation in the investigated springs. The northern part of the Tatra Mountains, though most intensively calcifying springs have the very ephemeral, provide an ideal site for lowest SI values and the Ca 2+ concentrations studying biogenic processes. The inorganic are also among the lowest (Table 2). Common factors alone do not seem to provide favorable for all the precipitating springs are very low conditions for calcite precipitation in the water efficiency within the range of 0.1-1 l/s investigated springs.

Springs with active calcium carbonate precipitation in the Polish part of the Tatra Mts. 225

Conclusions

1. Active calcite precipitation was found in resulted in calcite precipitation. The calcium the Polish part of the Tatra Mts. in eight precipitation is enhanced by dense moss springs located in Olczyska Valley (Dolina carpets growing in the spring areas. Olczyska), lower parts of Lejowa Valley 3. Two types of calcite precipitating (Dolina Lejowa) and in Ko ścieliska Valley springs were distinguished. Two springs (at the (Dolina Ko ścieliska). bottom of Olczyska Valley and on Adamica 2+ – 2. The highest amount of Ca and HCO 3 slope in Ko ścieliska Valley) represent long ions in water relative to other springs localized term accumulation of calcium carbonate, in Tatra Mts., localization at relatively low forming tufa deposits. In the other springs attitudes (up to ~1200m) as well as low water occasional calcite precipitation occur resulting efficiency are probably the three main abiotic in calcite encrustation of lower, water soaked factors that meet together in these springs, parts of the moss.

Acknowledgements

We are grateful to the authorities of the reviewer is thanked for helpful suggestions and Tatra National Park for providing the comments. permission for field work. The anonymous

References

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