The study area (Figure 1) forms a part of the Kolar schist belt which is/was
Figure 1. Geological sketch map of part of Kolar Schist belt showing plant and soil sample locations.
known for its world class lode gold deposits which are now almost exhausted due to continuous mining for over 100 years. This auriferous belt is made up of abundant metavolcanic sequences and thin metasedimentary intercalations of BIF. The BIF is chiefly confined to western boundary of the belt. Few ultramafic sequences have also been found to be present in this belt. The gold bearing lodes were mainly in the form of quartz-carbonate veins with commonly noticed sulphides like pyrite, pyrrhotite and arsenopyrite in the mineralized blocks. Carbonaceous schist horizons are found to be in close proximity with the gold bearing veins. Studies by Sivasiddaih and Rajamani  , Narayanswamy et al.  and Mukherjee,  provided lithological, structural and genetic aspects of Au mineralization in Kolar schist belt. The northern part of this belt, especially south of Srinivaspura, has been extensively lateritised (Figure 2) and the lateritic profiles appear as flat to undulatory features. The topography is by and large smooth with weathered bedrocks of pillowed (Figure 3) metavolcanics, sometimes exposed along nala cuts. Highly weathered lateritic areas in some places display cavernous structures (Figure 4), especially south of Nayakarahalli. River streams have low gradient and have dissected this country to produce shallow ravines. Several field traverses in the above said tracts revealed the presence of partially weathered sulphidic cherty layers (Figure 5) within the lateritized metabasaltic bedrocks. Lateritic soil and the enclosed cherty bands are drained by streams and the stream-sediments are panned by locals to extract gold fines/nuggets. This aptly reflects the auriferous nature of cherty BIF-bearing metavocanics in the studied area. The insitu enrichment of gold in laterites is also reported elsewhere, especially from Nilambur  and Chinmulgund  areas. The pillowed nature of basaltic rocks which are frequently traversed by sulphidic cherty veins, and moderate to strong lateritization is good indications to infer that Au could be distributed in the weathered substratum/soil in the study area. Also, the
Figure 2. Lateritised metabasalt, south of Srinivasapura.
Figure 3. Partially weathered pillowed metabasalt near Nayakarahalli.
Figure 4. Cavernous structures in lateritic zones near Nayakarahalli.
plants which grow in this area, could have possibly up-taken gold, besides other metals, during their metabolic activity. In this background, the areas near Nayakarahalli, Jaderi, and Holur, south of Srinivasapura where lateritic profiles are well developed, though discontinuously, have been subjected for geobotanical and biogeochemical studies with the main objective of understanding metal concentration, especially gold, in plants and soil.
Figure 5. Weathered Cherty layer within the lateratised metabasalt near Nayakarahalli.
2. Sampling Method
A cursory study of the terrain was made before samples were collected. The procedure, as enumerated by Brooks  was followed during plant sampling. The density and homogeneity of different species were appraised to minimize sampling errors. The soil substratum was also checked for possible human contamination, since it has proximity to mining area. Field work and sampling were carried out during post monsoon time in the month of November. This was the time when most of the herb and shrub species showed their full blooming. Precaution was taken to complete the sampling work in minimum time to ensure the least climatic influence on elemental uptake by plants. A rectangular grid sampling pattern was followed for sampling. The density and homogeneity of vegetation was thoroughly evaluated before sampling. Precautions like sampling the same species of plants, sampling the same organs of plants, recognizing the same growth level of plants and similar appearance and health of the plants were kept in mind while sampling  . At selected points soil samples were also collected to correlate their trace element values with plant samples. Care was also taken to observe any visible signs of morphological anomalies in plant species.
3. Analytical Method
The dried and pulverized samples of plants were decomposed by hot acid treatment. 0.5 g plant sample was digested using 0.5 ml con. H2O2 and 4 ml con. HNO3 in a tefflon digestion vessel in a microwave digester for 20 minutes.
The soil samples were also digested in microwave digester. Firstly, they were ground to −200 mesh by jaw crusher and further fine-ground to −250 mesh by agate mortar. Coning and quartering were done prior to taking required amount of sample. 0.25 gm of soil sample was digested with 2.5 ml of HF and 2.5 ml of con. HNO3 using Teflon digestion vessel in the microwave digester for 25 minutes. After digestion they were filtered by Whatman’s No. 42 filter paper and made up to 100 ml and used as stock solutions. Subsequently they (both plant and soil samples) were analysed by AAS (GBC make). Merck AAS standards were used for calibration. Repeat analyses were done at five sample interval for accuracy and precision. The above mentioned method was used for analysis of Cu, Cr, Zn, Ni, Co, As, Mn and Mg. The results of the analyses for plant samples are listed in Table 1 and that of soil samples in Table 2.
However, for Au analysis, the pulverized plant and soil samples were ignited at 700˚C for 1 - 2 hours with aquarigia solution, twice followed by HCl solution. For this 5 ml MIBK (methyl iso butyl ketone) was added and shaken for 5 minutes. The organic layer was washed with 10 ml 0.6 N HCl and this organic layer was collected in a dry 10 ml flask and was subjected for gold analysis using GF- AAS (Graphite Furnace-Atomic Absorption Spectrometer) along with standards which were also extracted in MIBK and the unknown concentration of Au in samples were determined.
3.1. Vegetation Pattern
The studied area is moderately vegetated. It exhibits scrubby to semi-deciduous type vegetation. Though, the soil substratum is fairly well developed, vegetation growth is not dense, probably due to poor humus content and hard pan-like nature of lateritic substratum at many places and modest rainfall (annual around 700 mm). Another possible reason for poor vegetation could be the removal of essential nutrients during the lateritization process  . However, in valley portions and moderately lateritized metabasaltic areas, vegetation is fairly denser. The dominant plant species in the study area are shrubs followed by herbs with less frequency of tree species. The shrub species are mainly represented by Argyreia cuneata, Dodonaea viscosa, Carissa carandas, Ziziphus, Barleria buxifolia, and Atylosia scarbiocides and the herb species by Leucas ciliata, Pulicaria wightiana, Chromolaena odorata, Hyptis suaveolens, Tephrosia tinctoria, Trichodesma indicum, Stylosanthes fruticosa, Evoluvus alsinoides, Pavonia zeylanica, Orthosiphon diffusus, Waltheria indica and Stachytarpheta indica. Fairly good distribution of Grass species (lemon grass) is also observed but is normally found in areas of deep soil cover. The common tree species noticed is Acacia megaladena. Another sparsely distributed tree species is Dolichandrone atrovirens.
In the present study, sampling of plants and soil has been carried out in 3 blocks, viz, Nayakarahalli, Holur and Jaderi. All these 3 blocks, as mentioned earlier, are mostly characterized by lateritic soil, with a scrubby vegetation pattern. The soil surface is normally characterized by the presence of sub-rounded (resembling nodular) iron rich gravels. The sampling was carried out during
Table 1. Trace Element concentrations (in ppm) in plant species of study area.
November period, when both herbs and shrubs were showing their exuberance and obviously it reflected the optimal metal uptake possibilities. Due to the absence of specific mineralized zone, sampling was done with roughly rectangular grid pattern with more or less the same distance from one sampling spot to other. Though small outcrops of cherty reefs are observed, their continuity could not be traced, owing to weathering effects. Thus, the entire laterite ground had to be targeted for geobotanical study and sample collection. A brief description of plant species studied and sampled and their biogeochemical aspects have been provided below.
Table 2. Trace element concentration (in ppm) in soil samples.
3.2. Leucas ciliata
It is one of the most common herbs in the lateritic zones of Nayakarahalli. It is a small herb with long and slender leaves. It has more or less a uniform distribution and is fairly denser in occurrence. Eleven samples of this species have been analyzed for different metals. It is observed that most of the analysed metals are in lower concentration, which are close to or around background values. Cu (65 - 160 ppm), Zn (8 - 131 ppm), Ni (14 - 65 ppm) and Co (0 - 64 ppm) are in lower concentrations. Cr (14 - 162 ppm) and Mn (819 - 5513 ppm) show slightly higher to moderate concentrations. Very high As content is noticed in soils where Leucas ciliata is grown, but its uptake appears to be poor (10 - 62 ppm). Arsenic being an essential element for plants and sometimes toxic, it is likely that it is poorly up-taken by this species.
3.3. Dodonaea viscosa
It is quite denser in its occurrence, as it is a drought-resistant shrub, which can thrive even in extreme conditions. No significant morphological change could be observed in this flora. Seven analyzed samples of this species showed poor concentration of Cu (110 - 180 ppm), Zn (73 - 149 ppm), Ni (25 - 170 ppm) and Co (10 - 36 ppm). Mn is highly variable, as low as 765 to as high 1243 ppm (but, this variation is within the background range). Arsenic concentration of 1 - 9 ppm is noticed. Fairly higher Cr is noticed in soils at the sites where this species is thriving, but in the analyzed samples of Dodonea viscosa, its content is lesser (15 - 87 ppm). Mn content is higher than in soils.
3.4. Acacia megaladena
It is a tree species (Figure 6) growing to a modest height and is present in all the studied lateritic soils in Nayakarahalli, Jaderi and Holur. The metal up-take ability of this species seem to be high for Cr, Ni and Co, as they are in higher than background concentration, though they are much lower in comparison to their
Figure 6. Acacia megaladena near Nayakarahalli area.
concentration in soil. Only two of the six samples showed small concentrations of Zn (64 - 72 ppm), Cu (0 - 110 ppm) and Mn (292 - 7879 ppm). Arsenic shows poor to moderate content from 3 to 9 ppm.
3.5. Carissa carandas
This shrub (Figure 7) occurs in the entire studied area. It has fairly good distribution. It is a perennial species which grows up to 2 ft. Its leaves are simple, ovate and shining, with long thorns and it bears terminal inflorescence. In the present study, 4 samples from Nayakarahalli and one from Holur lateritic profiles have been collected. This species is found to exhibit normal growth without any significant morphological changes. From the point of metal accumulation, this species shows variable Cu content (0 - 130 ppm), moderate enrichment of Cr (26 - 74 ppm), and lower Zn (84 - 133 ppm), Ni (10 - 25 ppm) and Co (20 - 50 ppm). Mn is in moderate concentrations. Though arsenic values are lower (20 - 58 ppm), they are slightly above the background concentration. As such, this species does not show any preferential accumulation for any element.
3.6. Tephrosia tinctoria
It is a perennial shrub which shows fair distribution in the study area. This shrub grows to a height of 4 - 5 ft. Its leaf pattern is alternate. Four samples of this species from Nayakarahalli and two from Jaderi have been analyzed for their trace element content. Cu shows poorer and variable (0 - 180 ppm) values. Zn is almost absent in all the samples. No significant concentration for Cr, Ni and Co is observed. Mn is in the background range. Arsenic concentration is very poor (6 -
Figure 7. Carissa carandus in Holur area.
44 ppm), when compared to significant higher concentration of the same in soil. The metal uptake by this species is not well reflected compared to concentration of metals in soil.
3.7. Barleria buxifolia
Most part of the studied Nayakarahalli, Holur and Jaderi areas witness the growth of this plant. This perennial shrub (Figure 8) grows up to a height of 5 - 6 ft. It shows strong spines under the leaves which are ovate, and bears terminal inflorescence, and flowers are purple-blue in colour. Its growth features and morphological characteristics are normal and lateritic substratum does not seem to have any visible influence on this species. Its uptake ability of metals seem to be modest, like other floral species of the area. It has poor concentration of Cu (0 - 150 ppm), Cr (8 - 86 ppm), Zn (0 - 115 ppm), Ni (12 - 40 ppm) and Co (10 - 33 ppm). When compared to their concentration in soils, all of these metals are poorly reflected. Mn is fairly high in concentration and is comparable to soil concentrations. Arsenic content is very low, close to the background range.
3.8. Ziziphus Species
This species does not find homogenous distribution in the studied area. It is a spiny perennial shrub growing to a height of 5 to 6 ft with alternate leaves. Three species of this plant, one from Nayakarahalli and 2 from Holur have been sampled which show lower concentration of Cu (35 - 90 ppm), Zn (0 - 115 ppm), Ni (14 - 62 ppm), Co (12.16 ppm) and As (13 - 34 ppm). Higher concentrations of
Figure 8. Barleria buxifolia in Nayakarahalli area.
Mn (8116 - 17,271 ppm) is also reflected in this species.
3.9. Waltheria indica
This flora is noticed in the entire studied area but with less frequency. This shrub which grows to a height of 6 ft bears yellow flowers in the nodes. A sample each from Nayakarahalli, Holur and Jaderi have been analyzed and the analysis indicate very poor uptake of Cu (0 - 130 ppm), Co (12 - 20 ppm), Zn (15 - 339 ppm), Cr (34 - 86 ppm), Ni (15 - 42 ppm) and Mn (1152 - 3240 ppm). Arsenic values (13 - 23 ppm) are also around the background concentration. For most of the analyzed elements, soil concentrations are not well reflected in the plant species.
3.10. Trichodesma indicum
It is a perennial herb which shows fairly good distribution in Nayakarahalli and Jaderi areas. This herb grows to a height of 3 ft. From the point of metal up-take it is poor in Cu (0 - 130 ppm) and Co (10 - 16 ppm). Arsenic is also poorly concentrated (22 - 24 ppm). Mn is close to or less than the background range. Except for Zn and to some content Mn, no other metal is enriched in comparison to soil concentration.
3.11. Argyreia cuneata
This species thrives well around Nayakarahalli. It is a perennial shrub (Figure 9) and has lesser density of distribution. Its leaves are oblong and blunt. Bright
Figure 9. Argyreia cuneata in Nayakarahalli area.
purple coloured and funnel shaped flowers and soft silky haired stems are the characteristic features of this plant. Two samples of this flora around Nayakarahalli have been analyzed and found to contain moderate to poor Cu (85 - 100 ppm), Zn (0 - 60 ppm), Ni (30 - 40 ppm) and Co (18 - 20 ppm). Cr concentration is slightly higher than background range. Arsenic is also in small concentration (24 - 28 ppm). Mn content is relatively higher, but much lesser than background range.
3.12. Atylosia scarbiocides
It has a thin density of distribution and is noticed only in Nayakarahalli and Jaderi. It is a annual/perennial shrub which grows to a height of 2 - 3 ft. It bears alternative triplets type leaves and inflorescence. Samples from both these areas show near background values of Cu (120 - 140 ppm), Ni (10 - 45 ppm) and Co (10 - 13 ppm). A sample from Jaderi has showed slightly higher Zn (569 ppm), whereas the other from Nayakarahalli showed zero value. Arsenic was also zero in Nayakarahalli, but the other sample showed 2 ppm. Mn concentration is in the background range.
3.13. Pavonia zeylanica
In Nayakarahalli and Jaderi areas, this plant is infrequently noticed. It is a perennial herb (Figure 10) which normally attains a height of 3 ft. It is characterized by ovate type leaves, palmately veined with axillary type inflorescence. A sample from Nayakarahalli and another from Jaderi have been analyzed for different metals, and the data shows that it is poor in Cu (90 - 100 ppm) and Ni (16 -
Figure 10. Pavonia zeylanica in Jaderi area.
18 ppm). Zn is slightly higher (131 - 576 ppm) but still within the background range and Co is in moderate to slightly higher concentration (13 - 24 ppm). Mn has appreciable concentration. Arsenic is also very poor in concentration (6 - 21 ppm). This plant does not reflect proportionate concentration of metals when compared to metal abundance of soil.
3.14. Hyptis suaveolens
Infrequent occurrence of this species is noticed only in Jaderi area. Two samples of this species showed poor concentration of Cu (135 - 140 ppm), Cr (26 - 45 ppm), As (13 - 18 ppm) and Zn (0 - 223 ppm). Ni (30 - 34 ppm) and Co (17 - 20 ppm) also showed poor values. Mn values are below the background range.
A grass variety is commonly noticed in Nayakarahalli area. It blankets the surface in a patchy manner. No significant grass cover is evident in Jaderi and Holur. In the present study four grass samples from Nayakarahalli have been analyzed. All the metals appear to be depleted in the analyzed samples. Chromium showed slightly enhanced values (32 - 225 ppm) and Mn was close to or slightly enriched than background concentration.
Besides the above floral species which have specific distribution pattern, there are some random species that grow in the studied areas. They included Pulicaria wightiana, Pulicaria wightiana, Chromolaena odorata, Dolichandrone atrovirens Stylosanthes fruticosa, Evoluvus alsinoides and Orthosiphon diffusus. A sample of each of these species have been analyzed (Table 1), but no significant metal uptake or depletion in them is noticed, when they are compared with the metal concentration in other species of the studied areas. They do not either reflect the proportionate concentration of metal as compared with the soil substratum (Table 2).
4. Gold Concentration in Plant Species Growing over Lateritic Profiles of Nayakarahalli, Holur and Jaderi
As mentioned earlier, the stream sediments in the small rivulets draining the laterite profiles in the study area are known to yield Au fines and small nuggets, which indicated at the laterite-hosted gold which was either in cherty veins or released into lateritic substratum from bedrocks i.e. pillowed metabasalt. Limited analysis of Au has been carried out for a few plant and soil samples. Herb species like Leucas ciliata (2 samples), Hyptis suaveolens (2 sample), Pulicaria wightiana (1 sample), Tephrosia tinctoria (1 sample) and a tree species viz. like Dolichandrone atrovirens (1 sample) have been analyzed and the data is presented in (Table 3). Three soil samples have also been analyzed. The soil analysis showed very poor concentration (5 - 10 ppb) of Au. Though these values are slightly higher than the background, no appreciable enrichment could be deciphered. Contrary to this, plants have a fairly high concentration of Au. Leucas ciliata showed 37 and 83 ppb, Hyptis suaveolens 25 and 36 ppb, Tephrosia 86 ppb, Pulicaria wightiana 25 ppb and Dolichandrone atrovirens 68 ppb (Table 3). These values probably suggest that Au in soil was available in the form of humic salts, which enabled plants to up-take it. Compared to background of 5 ppb concentration level in plants, these values are very high, which suggested that the plants growing over lateritic substratum could able to effectively uptake it and this aptly reflected the auriferous nature of the area.
5. Discussion and Conclusions
Lateritic zones overlying metabasaltic bedrocks in the southern parts of Srini- vaspura i.e. Holur-Nayakarahalli-Jaderi constitute distinct terrain conditions for geobotanical and biogeochemical studies. A general flat nature of this terrain
Table 3. Au concentration (in ppb) in plants and soil.
and moderate drainage pattern constitute a plateau like landscape. Dispersion of metals in this type of conditions could be controlled/affected by 1) enrichment of certain elements and draining out of some during lateratization, 2) dispersion of metals from the underlying metabasalts by hydromorphic process and 3) dispersion of elements from the cherty horizons (which normally resist lateritization due to their high silica nature) by oxidation and gossanisation process. The geochemical characteristics at the metabasalt-laterite interface are expected to be more or less the same and the dispersion pattern would be more homogeneous, barring localized variations. But considering the spatial distribution, the lateritized zones have vast spatial extent compared to cherty horizons. This setting could promote variable metal dispersion especially from the point of gold and other chalcophile elements. However, distribution of elements in drainage sediments could have been affected by mixing process and obviously are normalized. Hence, it becomes difficult to appraise the dispersion pattern of Au from the point of their concentrations in drainage sediments, i.e. whether Au has been derived from lateritized soil or cherty intercalations. However, elements like Cu, Cr, Ni, Co, As and Mn contents form more homogenous pattern, because of the homogenous substratum and bedrock conditions (Figure 11). All the metals mentioned above are fairly in good concentrations in soil, except few samples. Some of the relatively soluble elements like Cu and Co could have also been drained during lateritization. Uptaking by plants of most of the metals like Cr, Ni, Co, As and Mn reflect that these elements existed in soil substratum mostly as oxides as these metals are susceptible for oxidation during their prolonged
Figure 11. Trace element values plotted for studied plant species.
atmospheric exposure. However comparatively lesser values of metals in plants in relation to soil (Figure 12) indicates their poorer uptaking ability, which in turn could have been controlled by many biotic and abiotic factors, besides climatic influences prevailed in the terrain. Exceptionally, some species have absorbed high Mn. Similarly, high value of Zn seen in Pavonia zeylanica is only an isolated high but not high enough to be anomalous. Almost the background range of Au as inferred from very limited analysis reflects poor and uneven distribution of this metal in soil. However, plants express Au content in a better way (25 - 86 ppb). This is because, Au probably existed as colloidal particles adhering to iron hydroxides in soil. Humic acid activity could have influenced to make Au content available as colloidal particles to be present as adsorbed ions around iron oxides. Obviously, an inverse relation of Au concentration could be seen in the study area where poor concentration in soil and high concentration in plant is evident. Further, detailed biogeochemical studies could throw more light into the possible auriferous horizons underneath.
The authors thank Bangalore University for the financial support to carry out this work through a research grant. Mr. R. Nijagunaiah, Department of Botany, Bangalore University is gratefully acknowledged for his help in identifying the plant species both in field and laboratory. Dr. A. K. Roy, Regional Director,
Figure 12. Average metal concentration of plants plotted against average of soil samples.
and his collegues Dr. Premdas and Dr. Anitha Mary of AMD, Bangalore and Mr. K. B. S. S. Seetharam of M/s Shiva Analyticals Pvt. Ltd., for extending facilities for gold analysis. Mr. S. Santhosh, Ph.D. Scholar in the Department of Geology, Bangalore University is acknowledged for his assistance in preparing figures, tables and graphs.