CrawZealand & Beckett—Water and sediment chemistry Research, of Sutton Salt Lake New Journal of Marine and Freshwater 2004, Vol. 38: 315–328 0028–8330/04/3802–0315 © The Royal Society of New Zealand 2004 315 Water and sediment chemistry of Sutton Salt Lake, east Otago, New Zealand D. CRAW S. BECKETT Geology Department University of Otago P.O. Box 56 Dunedin, New Zealand email: [email protected] Abstract The Sutton Salt Lake is the only saline lake in New Zealand, and has formed in a windy cool-temperate maritime climate. Consequently, the lake is distinctly different from most of the world’s saline lakes that form in arid continental settings. Sutton Salt Lake forms annually in a shallow (5 m) bedrock-floored depression c. 50 km from the nearest coast. The site receives c. 500 mm/year rainfall compared with coastal rainfall of near 1000 mm/year because of a minor rain-shadow effect of coastal hills. Surface evaporation rate is high (c. 700 mm/ year) because of frequent strong winds. Sediments on the lake floor are derived by rain and wind erosion of the surrounding quartzofeldspathic schist bedrock, with a contribution from organic sources, particularly ostracods, and evaporative halite. The sediments have a higher proportion of phyllosilicates (muscovite, kaolinite, and chlorite) than the source rocks because of differential transport of these minerals into the lake depression. Lake water is entirely derived from rain, rather than groundwater, and the lake waters have had minimal chemical interaction with bedrock. Lake water pH is near 9 and pH of pore waters in drying lake sediments is near 8, compared with a pH near 7 for regional surface and ground waters. When full, the lake has salinity about one quarter to one third of that of sea-water, and ion ratios are similar to sea-water. The lake salinity is derived from marine aerosols in rainwater concentrated by c. 20 000 evaporation and refilling cycles in the lake depression. M03094; Online publication date 8 June 2004 Received 10 December 2003; accepted 5 April 2004 Keywords saline lake; geochemistry; marine aerosol; evaporite INTRODUCTION Most evaporative salt lakes form in continental areas with arid climates, such as inland western North America, Australia, and Antarctica (Eugster 1980; Chivas et al. 1991; Gibson et al. 1991). Well defined dry seasons with low humidity ensure evaporation of sparse and rare inputs of water in these environments. Saline lakes are widespread in these settings, and their sediments can coat valley floors over tens or hundreds of square kilometres. Gypsum is one of the most common evaporite minerals in these saline lakes (Eugster 1980; Chivas et al. 1991). Small land masses surrounded by ocean typically have humidity too high, and excess of rainfall over evapotranspiration, for development of evaporative salt lakes. However, this study describes a salt lake, Sutton Salt Lake, which has developed in southern New Zealand’s cool-temperate maritime climate. The lake is small (c. 2 ha) and is the only saline lake in New Zealand. Hence, the Sutton Salt Lake is unique in its setting. The lake site hosts halophytic vegetation around the lake margin, and diverse native fauna, making the site significant for biological and geological reasons (Bayly 1967; Murray 1972; Patrick 1989; Luxford 2001). Despite the biological significance of the lake area, little information on the chemistry of the substrate has been published even though the site owes its uniqueness to chemical processes. Bayly (1967) mentions some chemical characteristics in passing, and McIntosh et al. (1990) document some basic facts on the site. This study attempts to fill this knowledge gap by presenting descriptions of sediments and waters, and evaluating that data in the context of the geological and geographical setting of the lake. In particular, we focus on lake water and sediment chemistry, and examine these analytical results in terms of minerals and rocks that surround the lake, and potential external inputs to the lake. 316 New Zealand Journal of Marine and Freshwater Research, 2004, Vol. 38 Fig. 1 Digital elevation model (from www.geographx.co.nz) showing the topography of east Otago, New Zealand, and the location of Sutton Salt Lake at the southern end of the Middlemarch Basin. Inset shows east Otago in the South Island of New Zealand, and the location of the inland Mackenzie Basin where rainfall chemistry was obtained (Jacobson et al. 2003). REGIONAL SETTING Geology and topography The Sutton Salt Lake occurs near the southern edge of the Middlemarch Basin (Fig. 1), a structural depression on the downthrown side of the active Hyde Fault (Jackson et al. 1996). The basement rock of the area is Otago Schist, locally overlain by remnants of a veneer of Tertiary marine and nonmarine sediments. More remnants of these sediments underlie the Middlemarch Basin where they are covered by Quaternary gravels of the Taieri River (Fig. 1) and alluvial fans from rising marginal schist ranges. The regional Waipounamu Erosion Surface (LeMasurier & Landis 1996) is cut into the schist basement and has resulted in widespread low relief surfaces, which dominate the topography of the area around the Middlemarch Basin (Fig. 1). This erosion surface has been deformed by late Tertiary collisional tectonics to give rise to the complex set of ranges and basins of east and central Otago (Fig. 1; Jackson et al. 1996). Broad low relief uplands that separate the Middlemarch Basin from coastal Otago (Fig. 1) resulted from the same tectonism. The basement schist is coarse grained (>100 µm) and highly segregated into micaceous and quartzofeldspathic laminae on the mm to cm scale. The schist consists of quartz, albite, muscovite, chlorite, epidote, titanite, and calcite, with minor pyrite. Secondary calcite and pyrite are common along fractures in unoxidised schist. The schist beneath the erosion surface was intensely altered to a predominantly kaolinite-quartz assemblage, up to 20 m vertically, by groundwater within the sedimentary veneer (Craw 1994). Depth of alteration varied, and was controlled by subtle lithological variations in the schist. Alteration at the erosion surface resulted in varying degrees of oxidation of the schist, resulting in decomposition of chlorite and pyrite to kaolinite and brown iron oxyhydroxide. The kaolinitic rock was rapidly removed when the erosion surface was exhumed, and an undulating Craw & Beckett—Water and sediment chemistry of Sutton Salt Lake 317 Fig. 2 Contour map (m a.s.l.) of the Sutton Salt Lake catchment, east Otago, New Zealand, and immediately adjacent drainage areas, constructed using differential global positioning system. Heavy dashed line defines the drainage divide around the salt lake catchment. basement surface, studded by brown-stained schist tors, resulted. The steep-sided tors are typically 5– 10 m high and are separated by broad smooth depressions 20–100 m wide, containing sandy soils and colluvium generally <2 m thick. Tors and intervening depressions form a linear pattern trending north-west (Fig. 2) reflecting the underlying schist structural and lithological control, described as “gefugerelief” by Turner (1952). The Sutton Salt Lake is impounded by bedrock in a depression between tor ridges. There are many similar depressions that can contain ephemeral lakes in the vicinity (Fig. 2), but none of these others is saline. These other lakes are dammed by colluvium in depressions between lines of tors. Lake water apparently leaks slowly through this colluvium and escapes along depressions into the stream system. Ba 895 558 697 846 Cr 160 57 394 65 V 100 80 86 106 Zn 119 112 96 123 Y 34 31 30 34 Zr 197 182 262 178 Lake sediment 1 Lake sediment 2 Lake sediment 3 Lake sediment 4 Lake sediment 1 Lake sediment 2 Lake sediment 3 Lake sediment 4 Sr 273 322 281 254 Rb 148 136 112 160 Trace elements (ppm) Pb Ni Cu 31 32 37 27 32 36 22 34 42 34 33 39 As 11 8 8 13 Total 98.80 99.19 99.40 99.36 LOI 6.86 7.25 5.24 5.37 P2O5 0.24 0.30 0.18 0.19 K2O 3.89 5.17 4.66 4.70 Na2O 2.98 1.90 2.37 2.38 Major elements as oxides (wt%) MnO MgO CaO 0.07 2.35 2.47 0.15 2.80 3.91 0.09 2.35 1.70 0.09 2.31 1.81 Fe2O3t 4.69 6.46 6.05 6.10 Al2O3 16.00 18.57 18.12 18.43 Wet lake sediments were sampled from a range of sites over the lake while it was full in January 1998. These sediments were dried in an oven at 60°C, then powdered with an agate mortar and pestle. The powders were analysed for major, minor, and selected trace elements (Table 1) by X-ray fluorescence spectrometry in the Geology Department, University of Otago, using international standards (Craw et al. 2000). Major and minor elements were determined on fused discs, and trace elements were determined with pressed powder discs. Loss on ignition (LOI) was determined from weight loss after heating at 1100°C for 2 h. Chlorine (Cl) analyses were obtained for sediments sampled in November 1998 on dry parts of the lake bed. Samples were taken at dry surface, 10 cm deep, and 35–50 cm deep, at two localities 50 m from the lake edge. Cl analyses were determined by titration (oxygen-filled flask method) by the Microanalytical Laboratory, University of Otago, with detection limit of c. 0.2 wt%. Sulfur (S) analyses were obtained on a representative set of surface and deep (c. 50 cm) TiO2 0.68 0.72 0.71 0.73 METHODS SiO2 58.57 51.96 57.93 57.25 Climate The Sutton Salt Lake lies inland of two ranges of hills, and rainfall is lower than at the nearby Otago coast (Fig. 1), which receives c. 1000 mm/year. The lake area is essentially devoid of forest and is vegetated principally with native and exotic grasses. Temperatures typically range from lows of –10°C in winter to +30°C in summer, with occasional extremes beyond this range. The barren landscape is subject to regular strong winds, particularly in the spring (Edwards et al. 1988). The strongest and most common winds are from the north-west and southwest, with hourly mean speeds up to 25 m/s recorded 20 km to the west (Edwards et al. 1988). Wind may have contributed to formation of the tor topography (Fahey 1981), and wind erosion has been implicated in formation of saline depressions in the area (Raeside 1949). The east Otago uplands receive c. 500 mm/year precipitation, mainly as rain (Bayly 1967; Allen et al. 1997; Craw & Nelson 2000). Rain events arise with winds from the east, north-west or south-west, but the surrounding hills (Fig. 1) cause a rain-shadow effect for all winds. The surface can lose up to 700 mm/year moisture via evaporation (Bayly 1967; Allen et al. 1997; Craw & Nelson 2000), and surface water loss is especially rapid in warm dry north-west winds. Ce 136 69 112 119 New Zealand Journal of Marine and Freshwater Research, 2004, Vol. 38 Table 1 Representative X-ray fluorescence analyses of lake sediments for Sutton Salt Lake, east Otago, New Zealand. (All iron is calculated as ferric. LOI, loss on ignition.) 318 250* 250* 250* 250* 250* 250* 250* 250* 250* 250* 250* 250* 1000 920 850 1030 747 734 737 740 727 717 707 549 523 100* 100* 100* 505 509 476 459 –1.9 3.5 3.9 5.7 4.9 3.9 2.4 1.8 1.1 5.7 3.0 7.3 2.9 0.6 4.0 4.2 1.48 1.47 1.48 1.46 1.46 1.39 1.41 1.7 1.7 0.15 0.16 0.09 1.44 1.46 1.41 1.42 3.65 3.63 3.64 3.62 3.6 3.47 3.47 3.27 3.24 0.34 0.22 0.14 3.65 3.71 3.54 3.56 –2.07 –2.08 –2.07 –2.1 –2.09 –2.08 –2.06 –1.68 –1.66 –1.7 –1.63 –1.48 –1.39 –1.45 –1.45 –1.35 –3.16 –3.15 –3.14 –3.18 –3.11 –3.11 –3.11 –3.44 –3.42 –3.52 –3.37 –3.71 –2.29 –2.36 –2.41 –2.37 319 * Denotes analyses at or marginally above detection limit of method. 7610 8230 8310 8720 8670 8630 8540 5490 5660 5310 6280 4430 23400 21100 20600 21700 176 170 174 174 167 171 170 50 50 59 58 82 509 458 418 453 64 63 65 62 63 64 67 119 125 94 128 148 156 141 145 159 5070 4890 4880 4940 5000 5080 5180 3470 3610 2940 3660 2250 13400 12730 11550 12150 111 109 108 109 108 109 109 85 88 87 113 70 713 642 608 635 (halite) SI (calcite) (dolomite) (gypsum) % error alk. SO42– Cl– Mg2+ Ca2+ Na+ K+ pH 9.1 9.1 9.1 9.1 9.1 9.0 9.0 9.1 9.1 8.2 8.1 7.9 9.0 9.1 9.0 9.0 lake lake lake lake lake lake lake lake lake pores pores pores lake lake lake lake Jan 1998 Jan 1998 Jan 1998 Jan 1998 Jan 1998 Jan 1998 Jan 1998 Nov 1998 Nov 1998 Nov 1998 Nov 1998 Nov 1998 Aug 2003 Aug 2003 Aug 2003 Aug 2003 Table 2 samples. S contents were determined by a PerkinElmer Elemental Analyser in the Microanalytical Laboratory. About 5 mg of powdered sample was heated to 1100°C for analysis, and detection limit was c. 0.02 wt%. Water samples were collected in plastic bottles from the lake, and these waters were filtered before analysis for principal cations and anions. Seven samples from different points in the lake were taken in January 1998 when water was c. 50 cm deep, and an additional two lake water samples were obtained in November 1998. Four more samples of water were taken from remnant pools when the lake was almost dry in August 2003. Saturated sediments taken at three of the sampling sites in November 1998 were centrifuged to release pore waters, which were also analysed (Table 2). Initial water analyses (Table 2) were done by University of Otago Chemistry Department, and the August 2003 analyses were done by Chemsearch, an internationally accredited laboratory in the Chemistry Department. Charge balance errors for the analyses are shown in Table 2. APHA (1995) method 3111B was used for Ca2+, Mg2+, Na+, and K+, 4500–Cl C for chloride, and 2320B for dissolved carbonate. Detection limits for these common ions are c. 1 mg/litre, and analyses for these ions are reproducible to less than 1% error in the compositional ranges observed at Sutton Salt Lake. Initial sulfate analyses were done by nephelometry, with a detection limit of c. 200 ppm, and only trace amounts were detected in the dilute lake waters. The more concentrated August 2003 waters were analysed for sulfate by ion chromatography (Metrohm column) at Chemsearch, and again by ion chromatography (Dionex column) at Hill Laboratories, Hamilton, New Zealand. The August waters were also analysed for total S by ICP at Hill Laboratories and results converted to sulfate assuming all dissolved S is sulfate. Results for the two latter methods of sulfate analyses agree within 10% of the Chemsearch values, and the Chemsearch results (1 mg/litre detection limit) are presented in Table 2. Analytical error lies within the size of the symbols in all diagrams in this paper. Water pH was determined with an Oakton portable pH meter calibrated with standard pH solutions. Additional waters were collected from small streams between the east Otago coast and the Middlemarch Basin, for comparison with the lake waters. These waters Analyses of lake waters and pore waters. (SI, modelled saturation index, log scale; alk., alkalinity as HCO3– ; % error is charge balance error in analyses.) Craw & Beckett—Water and sediment chemistry of Sutton Salt Lake 320 New Zealand Journal of Marine and Freshwater Research, 2004, Vol. 38 Fig. 3 Composite section (centre) through the sediments on the floor of the Sutton Salt Lake, east Otago, New Zealand, as measured in pits dug in the dry lake bed. Chlorine concentrations in two profiles through the sediments are depicted on the left. Pie diagrams on right depict the principal constituents of the surface layer: upper pie shows the grain size distribution, and lower pie shows the proportions of constituents in the sand fraction. were analysed for Na+ and Cl– in the Chemsearch laboratory by the above methods. The mineralogical nature of a representative sample of lake sediment was determined by dry sieve separation (63 µm) of sand and finer material. The calcareous content of the sand fraction (containing abundant ostracods) was calculated from weight loss after addition of hydrochloric acid, and the organic content then determined by weight loss after treatment with hydrogen peroxide. The remnant terrigenous sand was examined optically and by Xray diffraction. The fine component (lacking ostracods) was characterised by X-ray diffraction in the samples taken from the lake bed in January 1998 (above). Surface salt encrustations and associated dry surface sediments were also characterised by Xray diffraction. SUTTON SALT LAKE The Sutton Salt Lake is an ephemeral lake that lies in a c. 5-m-deep depression between two lines of tors, c. 300 m from the edge of the Middlemarch Basin (Fig. 2) and c. 250 m a.s.l. (Fig. 3). The salt lake is 150 m wide and 340 m long, and is elongate parallel to the tor lines (Fig. 2, 3). Schist crops out at or near the lake margins, and the lake is apparently dammed by schist all round. The lake dries up during most summers, apart from pools after rainstorms, and refills during the following winter. However, the lake can remain full over wet summers, and this was so for the first season of this study (summer of 1998– 99). When full, the lake is 40–50 cm deep, with little variation in depth over the whole depression. Waves >40 cm high build up on the lake on windy days, and the water readily becomes turbid and discoloured as bottom sediment is stirred. When empty, the lake depression becomes a flatbottomed muddy plain with extensive formation of polygonal desiccation cracks on the 10–50 cm scale. Desiccation cracks extend c. 10 cm below the surface. A halite crust develops on the dry surface, and halite films float on thin (cm scale) water remnants. Gypsum is a trace component of some Xray diffractograms of crusts. The upper 10 cm of sediment contains abundant ostracods, and the ostracod component decreases to low levels below 10 cm. The lake depression contains c. 50 cm of sediment (Fig. 3), and sediment thickness varies little Craw & Beckett—Water and sediment chemistry of Sutton Salt Lake 321 Fig. 4A–D Whole rock major element geochemical comparisons between lake sediments below the surface layer (black diamonds), and fresh basement schist (open squares) nearby at Barewood (Fig. 1). over the whole depression. The sediments are unstratified and massive because of bioturbation, wave disturbance, and historic farm animal incursion. Angular schist blocks up to 8 cm across are irregularly distributed at and near the base of the lake sediment column, and larger boulders (m scale) occur near the lake margin. Lake sediments are dominated by silt and clay grains (80–90%; Fig. 4), with the remainder being fine sand. The silt and clay is predominantly muscovite and kaolinite, with minor chlorite, quartz, and feldspar. The sand-size fraction (Fig. 4) is c. 70% terrigenous, consisting of quartz, albite, muscovite, and kaolinite, with minor chlorite, derived from the schist basement. The remaining 30% is made up of calcareous material and organic material in subequal proportions (Fig. 3), all of which is derived from ostracods. LAKE SEDIMENT COMPOSITION Throughout the following descriptions, Sutton Salt Lake sediment compositions are compared to the basement schist from which most of the sediment was derived (above). A set of analyses of schist from the Barewood area (Fig. 1; MacKenzie 1990) is used for this purpose. The Barewood schist is lithologically similar to that at Sutton Salt Lake, and lies directly along strike from the lake. The Barewood samples were taken from fresh outcrops and drill cores, and therefore represent unweathered schist. The lake sediments contain only 50–65% silica, which is generally lower than Barewood schists, and relatively high titanium (Fig. 4A). As such, the lake sediments chemically resemble the more micaceous parts of the basement schist schists (Mortimer & 322 New Zealand Journal of Marine and Freshwater Research, 2004, Vol. 38 Roser 1992), rather than the more quartzofeldspathic schists that the Barewood samples represent. There is minor enrichment of iron (Fe) and magnesium (Mg) in lake sediments compared to most samples of schist bedrock, but the range in Fe2O3 and MgO analyses is similar for sediments and schist (Fig. 4B). Lake sediments as a group have generally higher potassium (K) content than Barewood schists, but there is considerable overlap of sodium (Na) contents (Fig. 4C). There is a distinct antithetic relationship between K2O and Na2O in lake sediments (Fig. 4C). The basement schists have a wide range of calcium (Ca) contents and the lake sediments show similar high and variable CaO (Fig. 4D). Likewise, the “loss on ignition” that mainly includes CO2 and H2O is variable (2–4 wt%) in both bedrock schists and the lake sediments. Most trace element concentrations are similar in Barewood schists and the lake sediments (Table 1), although both chromium (Cr) and lead (Pb) contents are slightly elevated in the lake sediments compared to the bedrock schist. Sulfur contents of six lake sediments are nearly all at the detection limit of the analytical method: 0.02 wt%. The highest measured value is 0.17 wt%. There was no systematic difference between samples taken from the surface or from up to 50 cm depth. The observed S contents of the lake sediments are similar to, or lower than, those of nearby unmineralised Barewood schists (typically 0.1–0.2 wt% S). WATER CHEMISTRY Sutton Salt Lake waters have distinctive chemistry (Table 2), and in this section these waters are compared with other waters from the region to emphasis the key points of the lake water chemistry. The sea is the largest water reservoir in the area, so this is used as one point of comparison (Wilson 1975). Sea-water components migrate inland via marine aerosols in the atmosphere, deposited as rain, so rainwater composition is relevant for comparison. An analysis of rainwater in an inland rain-shadow area (Jacobson et al. 2003) is used for this comparison. Likewise, we compare the lake waters with surface waters having a substantial rainwater component from the Taieri Basin, immediately south of the Sutton Salt Lake (Fig. 1). The data set used, from Litchfield et al. (2002), includes waters with a wide range of dissolved loads, including two samples that may have a tidal influence. We also compare lake waters with groundwater in the schist basement, Fig. 5 Spatial and temporal variation of pH in Sutton Salt Lake (east Otago, New Zealand) wet sediments in November 1998, measured in a traverse from the shore (m scale, open squares) and in sections through the sediments in pits (cm scale, black diamonds). Water pH in January 1998 is indicated with an open rectangle. Typical regional surface and groundwater pH range is indicated with black bar (lower left). using a set of analyses from near Macraes Flat (Fig. 1; Craw & Nelson 2000). The pH of the water in the lake when it is full is consistent at 9.0 to 9.1 across the lake (Fig. 5). When the lake was nearly dry, pH of the saturated sediments was measured at sites progressively farther from the shore, and at various depths in pits dug in the sediments. These data (Fig. 5) show that the pH ranged from 7.7 to 8.4, with no systematic variation with position in the lake. All pH measurements are at or above the highest levels normally observed in surface waters and groundwaters in the region (Fig. 5). The analysed lake waters are dominated by Na+ and Cl– (Table 2), and these two ions are present in approximately equal molar concentrations (Fig. 6A). There is a slight excess of Cl over Na, similar to that observed in sea-water (Fig. 6A). The Na+/Cl– ratio of the lake water is different from the distinct Na+ enrichment observed in groundwater in the schist bedrock (Craw & Nelson 2000; Fig. 6A). K+ and Mg2+ are approximately constant at c. 110 and 170 ppm respectively in the January 1998 (full) lake waters, but lake and pore waters sampled at other times are different from the earlier samples and more variable (lower in November 1998 and higher in August 2003; Table 2, Fig. 6B). The Ca2+ content of all analysed waters is 60–150 ppm, in contrast to highly variable alkalinity which ranges from c. 100 to 740 ppm (Fig. 6C). With respect to sulfate and Craw & Beckett—Water and sediment chemistry of Sutton Salt Lake 323 Fig. 6A–D Lake water chemistry (black diamonds) compared to sea-water (black square) and groundwater in the basement schist (black triangles). Large open circles in D are waters from the Taieri Basin (Fig. 1). sodium, Taieri Basin groundwaters form a trend of varying degrees of dilution towards sea-water because of marine aerosol deposition (Fig. 6D; Litchfield et al. 2002). The Sutton Salt Lake waters lie slightly on the sodium-enriched or sulfatedepleted side of the concentrated end of this trend (Fig. 6D). DISCUSSION Source of lake sediment The composition of the lake sediments is generally similar to that of the basement schist (Table 1; Fig. 4). These similarities in composition, combined with observations of schist minerals in the sediment, confirm that most of the sediment has been derived by erosion of the surrounding schist. However, there are some minor differences between basement schist and lake sediments that indicate that there has been some fractionation of schist debris during erosion and transport. The trend from high silica, low titanium to low silica, high titanium (Fig. 4A) is characteristic of decreasing proportions of quartzofeldspathic component and increasing proportions of micaceous component of the schist (Mortimer & Roser 1992). The enrichment in titanium in micaceous material arises because titanite, the main titanium mineral, occurs principally as micron-scale grains dispersed through the micaceous segregations. We infer from these data that erosion and transport of bedrock material into the lake has resulted in minor enrichment in micas, and relative depletion in the 324 New Zealand Journal of Marine and Freshwater Research, 2004, Vol. 38 Elevated CaO and LOI in the lake sediments and some schists arises from the variable component of calcite: calcareous and organic ostracod material in the sediments (Fig. 3), and calcite veins in the basement schists. Calcite veins are readily removed from schist outcrops by weathering, and outcrops at Sutton Salt Lake have fewer remaining calcite veins than the fresh rocks at Barewood. Hence, the variability of CaO and LOI in the lake sediments reflects the variability of ostracod component, rather than the schist source material. Fig. 7 Sketch map of east Otago, New Zealand, showing molar Na/Cl ratios of surface waters in streams and small lakes, and some shallow groundwaters. Most sites have Na/Cl near 1, reflecting rainout of marine aerosols. High Na/Cl reflects water-rock interaction with basement schist. quartzofeldspathic component. This is in accord with direct observations of the sedimentary material that confirm a high mica component (above). The general elevation of K2O content in sediments (Fig. 4C) results from the same increase in micaceous component during sedimentation inferred above. The inverse relationship between K2O and Na2O in the sediments (Fig. 4C) directly reflects relative enrichment in muscovite and depletion of albite in the sediments compared to the schist basement. Chlorite is the principal Fe-Mg mica, but muscovite also contains significant Fe and Mg in these schists (Brown 1968). Enrichment in these micas therefore accounts for the minor and inconsistent elevation in Fe2O3 and MgO in the sediments (Fig. 4B). Cr occurs principally in solid solution in chlorite in the Otago Schist, and the slightly elevated Cr in the lake sediments may reflect decomposition of chlorite in the weathering environment. Pb enrichment may arise from similar processes. Rainwater and schist water-rock interaction The Sutton Salt Lake has strongly elevated levels of dissolved constituents, even when full, compared with nearby water bodies. The two most plausible potential sources of dissolved constituents in saline lakes are from rainwater that has chemically interacted with the underlying rocks (e.g., Eugster 1980), or from direct input of rainwater containing dissolved salts (e.g., Chivas et al. 1991). Both of these sources of water involve rainwater input. The dissolved constituents in inland South Island rainwater are dominated by marine aerosols, with a Na+/Cl– ratio of near 1 (Ahlers & Hunter 1989; Jacobson et al. 2003), similar to that seen nearer the coast (Litchfield et al. 2002; above). Na+/Cl– ratios in streams in the hills between Sutton Salt Lake and the sea reflect the marine aerosol input from rainwater (Fig. 7). Hence, we can evaluate the two potential sources of dissolved constituents with reference to the composition of sea-water and marine aerosols in rain. Chemical interaction between water and schist bedrock results in progressively increasing Na+ content of the water from dissolved albite, whereas Cl– remains essentially constant, so the Na+/Cl– ratio rises (Fig. 6A,D; Craw 2000; Craw & Nelson 2000). Dissolution of calcite during water-rock interaction results in elevated Ca2+ and HCO3– in the groundwater (Craw 2000; Craw & Nelson 2000). At the same time, decomposition of chlorite increases the dissolved Mg content, and shallow groundwaters commonly have a Ca2+/Mg2+ ratio near 2 (Craw 2000; Litchfield et al. 2002). Hence, water that has had significant interaction with schist becomes dominated by Ca2+ and HCO3–, with subordinate Na+ and Mg2+, and only minor Cl–. Evaporative deposits associated with near-surface schist groundwater seepages are dominated by calcite, with minor iron oxyhydroxide. Compositions of typical schist-hosted groundwaters from the Macraes Flat area (Fig. 1) reflect the above reactions, as shown in a Piper Craw & Beckett—Water and sediment chemistry of Sutton Salt Lake SO42-80 +Cl- 60 Fig. 8 Piper diagram comparing groundwater that has interacted with schist (black dots) with Sutton Salt Lake (east Otago, New Zealand) waters (black squares), and sea-water (open circles with crosses). 40 ground 20 water CC C C CC 2+ C CC C CC C C C C CC CC C C C C C C C C C C C C Mg 80 60 40 20 C C C C C CC C C C CC C C C CC C C C C C C C C C C C CC C CC Ca2+ diagram (Fig. 8). Stream waters in the Macraes Flat area generally have a higher Na+/Cl– ratio than coastal streams (Fig. 7) because Macraes Flat streams are fed mainly by groundwater, except during storms. In contrast, the most prominent feature of the Sutton Salt Lake geochemistry is the high Na+ and Cl– of the site, manifested as a halite crust when the lake is dry, and Na-Cl saline water when the lake is full. Sutton Salt Lake waters show no evidence for the water-rock interaction reactions described above. The observed water compositions, including pore waters, plot in tight clusters on the Piper diagram (Fig. 8). These tight clusters of data plot closely to sea-water compositions (Fig. 8). Hence, we conclude that the Sutton Salt Lake derives it salts from seawater via marine aerosols (Jacobson et al. 2003), and that the waters have had negligible chemical interaction with schist bedrock. Mineral saturation indexes Saturation indexes for common evaporite minerals in Sutton Salt Lake waters were calculated using modelling program PHREEQC (Parkhurst et al. 1980), and results are listed in Table 2. These model calculations show that the lake waters are typically strongly oversaturated with respect to calcite (>10 times) and dolomite (>1000 times). The sampled pore waters were not so strongly oversaturated with respect to these minerals, and approached UDD D 325 2+ 80 Ca +Mg2+ 60 40 sea-water D Sutton Salt Lake U D D SO4280 60 40 C C C C C C C C C C CC C C C C Na++K+ HCO3- U D D D Cl- equilibrium saturation levels (Table 2). Growth of ostrocods in the lake undoubtedly facilitates temporary removal of some dissolved Ca and Mg carbonate into the sediments. It is probably this biological activity that prevents precipitation of carbonate minerals in the evaporate crusts. Ephemeral carbonate crusts on rocks on the lake margin have been noted in the past (C. A. Landis pers. comm.), but were not observed during the present study. Halite and gypsum, the two minerals that have been observed in evaporite crusts on the dry lake bed, are distinctly undersaturated in even the most concentrated brines sampled in this study (Table 2). Differences of Sutton Salt Lake waters from sea-water The K and Mg contents of full lake water are similar to those of dilute sea-water, when corrected for differing Cl contents (Fig. 9A). K is relatively enriched in some lake sediment pore waters (Table 2), probably from localised dissolution of muscovite in the wet sediments. High K in rainwater from inland South Island (Fig. 9B; Jacobson et al. 2003) may be a result of dissolution of terrigenous particulate micaceous dust, and this phenomenon may contribute to elevated K in lake waters when rain events occur on a near-dry lake bed. Calcium is slightly depleted in Sutton Salt Lake waters compared with sea-water (Fig. 9A), yet 326 New Zealand Journal of Marine and Freshwater Research, 2004, Vol. 38 marine aerosols are typically enriched in Ca2+ compared with sea-water (Warneck 2000). The inland rainwater Ca2+ content (Jacobson et al. 2003) reflects this enrichment of Ca, and the Sutton Salt Lake waters are strongly depleted compared with that rainwater (Fig. 9B). However, lake sediment pore waters have higher Ca2+ than the lake waters (Table 2; Fig. 9C). This variation in Ca2+ is probably related to variable degrees of dissolution and uptake of calcium carbonate from ostracods. Most marine aerosols contain sulfate concentrations similar to, or greater than, sea-water (Warneck 2000), so molar SO42–/Cl– ratio of >0.1 should be expected in subsequent rainout (Fig. 9B). This is apparently true for surface waters on the Taieri Basin, where relatively high SO42–/Cl– ratios occur (Fig. 6D). Conversely, Sutton Salt Lake waters are slightly depleted in sulfate compared with seawater (Fig. 9A). Groundwater in schist bedrock readily dissolves S from dispersed pyrite and related decomposition products to maintain a low but significant dissolved sulfate content (Fig. 8, 9B; Craw 2000; Craw & Nelson 2000). Recharging surface waters in inland areas have low dissolved ion contents (Kim & Hunter 2001) and these waters rapidly develop a rock-controlled S content, as they do a rock-controlled Na content (above). This sulfate content is similar to that of many surface waters nearer the coast, and higher than Sutton Salt Lake waters (Fig. 9B). Since all of the likely sources of input water to the Sutton Salt Lake have significant dissolved sulfate, the minor depletion of S at the lake site implies that the S has preferentially left the site. This cannot have occurred via drainage of liquid water as other dissolved ions, especially Na+ and Cl–, would have left the site at the same time. A more plausible, although speculative, alternative is that the S was volatilised and left with evaporating water. The enrichment of marine aerosols in S compared to seawater (above) is a result of biological formation of dimethyl sulfide in the sea, and similar processes occur on land (Gibson et al. 1991; Warneck 2000). Saline mudflats can be particularly productive of volatilised S, mainly as H2S and dimethyl sulfide (Goldberg et al. 1981; Warneck 2000), and this environment may be a reasonable analogue for the biologically active surface of the Sutton Salt Lake. Timing of lake formation The Sutton Salt Lake depression formed during late Tertiary–Recent uplift of the schist basement and associated stripping of the Tertiary sediment veneer. Fig. 9 A, Comparison between sea-water and water from Sutton Salt Lake (east Otago, New Zealand) compositions, presented as molar ratios normalised with chloride. Black squares, lake full; open squares, lake almost dry. Diagonal line represents 1:1 correspondence in molar ratios between sea-water and lake water. B, Similar diagram to A, comparing sea-water and Mackenzie Basin (Fig. 1) rainwater (Jacobson et al. 1993). The Sutton area has been progressively rising since the late Miocene (Youngson & Craw 1996). The cool semi-arid inland climate developed as high (2–3 km) mountains rose along the western side of the South Island (Fig. 1) in the Pliocene (Chamberlain et al. 1999). Hence, the lake depression may be as old as Pliocene. Full lake water (e.g., January 1998, Table 2) could have formed from repeated evaporation and accumulation of rain containing marine aerosols of the concentration described by Jacobson et al. (2003). Mass balance calculations suggest that c. 20 000 cycles of complete evaporation followed by Craw & Beckett—Water and sediment chemistry of Sutton Salt Lake lake filling and redissolution of the evaporite crusts would be required to produce the observed salinity. The lake does not dry out every year, so this calculation indicates that the lake is more than 20 000 years old. Because of major climate changes in the late Quaternary and possible wide variations in aerosol contents of rain, no more detailed speculation using water compositions is warranted. CONCLUSIONS The Sutton Salt Lake is impounded by schist bedrock, and loses negligible amounts of water by drainage. Instead, water is lost by evaporation, encouraged by low rainfall and frequent dry winds. The lake depression is floored by sediment derived from the underlying schist and washed in by rainwater, with a minor halite crust when the lake is dry. Water chemistry data (Fig. 6, 8) show that there has been negligible input into the Sutton Salt Lake site of water that has chemically interacted with the schist bedrock. Comparisons to sea-water and rainout of marine aerosols (Fig. 8, 9A,B) suggest that rainwater is the dominant water source for the lake. Na, Cl, K, and Mg are contributed in approximately sea-water ratios, albeit highly diluted by rainwater. Formation of the lake required c. 20 000 cycles of evaporation to dryness followed by refilling of the lake and redissolution of the evaporite crusts. This is different from the mechanism for saline soil formation elsewhere in Otago postulated by Raeside (1942), in which groundwater plays a prominent role. ACKNOWLEDGMENTS This study was funded by the University of Otago. Discussions with C. A. Landis initiated the project, and his enthusiasm helped keep it going. Jon Kim contributed ideas and comments that helped with interpretations, and Sean Barker provided some Na and Cl analyses of surface waters. Chris Pearson assisted with GPS mapping of the lake site. Field assistance by Debra Chappell, Brian Jones, Mark Walrond, and John Becker, and laboratory assistance by D. Walls, greatly facilitated technical aspects of the study. Department of Conservation provided permission for access and sampling in the Sutton Salt Lake reserve. 327 REFERENCES Ahlers, W. W.; Hunter, K. A. 1989: A baseline survey of water quality and trace metals in the upper Manuherikia and Idaburn rivers, Central Otago. Energy Research and Development Report RD 8820. 112 p. Allen, R. B.; McIntosh, P. D.; Wilson, J. B. 1997: The distribution of plants in relation to pH and salinity on inland saline/alkaline soils in Central Otago. New Zealand Journal of Botany 35: 517–523. APHA 1995: Standard methods for examination of water and wastewater. 19th ed. Washington, D.C., American Public Health Association. Bayly, I. A. 1967: The fauna and chemical composition of some alhalassic saline waters in New Zealand. New Zealand Journal of Marine and Freshwater Research 1: 105–117. Brown, E. H. 1968: The greenschist facies in part of eastern Otago, New Zealand. Contributions to Mineralogy and Petrology 14: 259–292. Chamberlain, C. P.; Poage, M. A.; Craw, D.; Reynolds, R. C. 1999: Topographic development of the Southern Alps recorded by the isotopic composition of authigenic clay minerals, South Island, New Zealand. Chemical Geology 155: 279–294. Chivas, A. R.; Andrew, A. S.; Lyons, W. B.; Bird, M. I.; Donelly, T. H. 1991: Isotopic constraints on the origin of salts in Australian playas. 1. Sulphur. Paleogeography, Paleoclimatology, Paleoecology 84: 309–332. Craw, D. 1994: Contrasting alteration mineralogy at an unconformity beneath auriferous terrestrial sediments, central Otago, New Zealand. Sedimentary Geology 92: 17–30. Craw, D. 2000: Water-rock interaction and acid neutralization in a large schist debris dam, Otago, New Zealand. Chemical Geology 171: 17–32. Craw, D.; Nelson, M. 2000: Geochemical signatures of discharge waters, Macraes mine flotation tailings, east Otago, New Zealand. New Zealand Journal of Marine and Freshwater Research 34: 597–613. Craw, D.; Chappell, D.; Reay, A.; Walls, D. 2000: Mobilisation and attenuation of arsenic around gold mines, east Otago, New Zealand. New Zealand Journal of Geology and Geophysics 43: 373–383. Edwards, P. J.; Neilson, G. D.; Dawber, K. R. 1988: Windtower measurements and energy analysis at a potential aerogenerator site in Otago, New Zealand. New Zealand Energy Resources Development Committee Report 161. 328 New Zealand Journal of Marine and Freshwater Research, 2004, Vol. 38 Eugster, H. P. 1980: Geochemistry of evaporitic lacustrine deposits. Annual Reviews of Earth and Planetary Science 8: 35–63. Eugster, H. P.; Hardie, L. A. 1978: Saline lakes. In: Lerman, A. ed. Lakes: chemistry, geology, physics. New York, Springer-Verlag. Fahey, B. D. 1981: Origin and age of upland schist tors in Central Otago, New Zealand. New Zealand Journal of Geology and Geophysics 24: 399–413. Gibson, J. A. E.; Garrick, R. C.; Franzmann, P. D.; Deprez, P. P.; Burton, H. R. 1991: Reduced sulphur gases in saline lakes of the Vestfold Hills, Antarctica. Paleogeography, Paleoclimatology, Paleoecology 84: 131–140. Goldberg, A. B.; Maroulis, P. J.; Wilner, L. A.; Bandy, A. R. 1981: Study of H2S emissions from a salt water marsh. Atmospheric Environment 15: 11–18. Jackson, J.; Norris, R. J.; Youngson, J. H. 1996: The structural evolution of active fault and fold systems in Central Otago, New Zealand: evidence revealed by drainage patterns. Journal of Structural Geology 18: 217–234. Jacobson, A. D.; Blum, J. D.; Chamberlain, C. P.; Craw, D.; Koons, P. O. 2003: Climatic and tectonic controls on chemical weathering in the New Zealand Southern Alps. Geochimica et Cosmochimica Acta 67: 29–46. Kim, J. P.; Hunter, K. A. 2001: Geochemical cycling of major and minor elements in the Taieri River and Waipori River catchments. Journal of the Royal Society of New Zealand 31: 745–762. LeMasurier, W. E.; Landis, C. A. 1996: Mantle-plume activity recorded by low-relief erosion surfaces in West Antarctica and New Zealand. Geological Society of America Bulletin 108: 1450–1466. Litchfield, N. J.; Craw, D.; Koons, P. O.; Edge, B.; Perraudin, E.; Peake, B. M. 2002: Geology and geochemistry of groundwater within the Taieri Basin, east Otago, New Zealand. New Zealand Journal of Geology and Geophysics 45: 481–497. Luxford, A. P. 2001: Ecology of the Sutton Salt Lake scenic reserve. Unpublished MSc thesis lodged in the Library, University of Otago, Dunedin, New Zealand. McIntosh, P. D.; Beecroft, F. G.; Patrick, B. 1990: Register of saline soil sites in north and Central Otago, Volume 1. Division of Land and Soil Science, Technical Report 5. MacKenzie, D. J. 1990: Gold, tungsten and antimony mineralisation at Barewood, East Otago, New Zealand. Unpublished MSc thesis lodged in the Library, University of Otago, Dunedin, New Zealand. Mortimer, N.; Roser, B. P. 1992: Geochemical evidence for the position of the Caples-Torlesse boundary in the Otago Schist, New Zealand. Journal of the Geological Society, London 149: 967–977. Murray, E. 1972: Vegetation zonation at the salt lake near Sutton. Unpublished thesis lodged in the Botany Department Library, University of Otago, Dunedin, New Zealand. Parkhurst, D. K.; Thorenston, D. C.; Plummer, N. L. 1980: PHREEQE, a computer program for geochemical calculations. United States Geological Survey Water Resources Investigations 80– 96. 210 p. Patrick, B. H. 1989: Lepidoptera of salt pans of Central Otago. Report for Department of Conservation, Dunedin, New Zealand. Raeside, R. 1949: The origin of salt pans in Central Otago. New Zealand Journal of Science and Technology 30: 96–101. Stumm, W.; Morgan, J. J. 1981: Aquatic chemistry. New York, Wiley. 780 p. Turner, F. J. 1952: “Gefugerelief” illustrated by “schist tor” topography in Central Otago, New Zealand. American Journal of Science 250: 802–807. Warneck, P. 2000: Chemistry of the natural atmosphere. International Geophysics Series 71 (2nd ed). London, Academic Press. Wilson, T. R. S. 1975: Salinity and major elements of sea water. In: Riley, J. P.; Skirrow, G. ed. Chemical oceanography (2nd ed), Vol 1. London, Academic Press. Pp. 365–413. Youngson, J. H.; Craw, D. 1996: Recycling and chemical mobility of alluvial gold in Tertiary and Quaternary sediments, Central and East Otago, New Zealand. New Zealand Journal of Geology and Geophysics 39: 493–508.
© Copyright 2026 Paperzz