Nickel hyperaccumulation by natural plants in Turkish serpentine soils

Natural plants in Turkish serpentine soils were surveyed to determine their Ni accumulation capability. Geographic distribution and diethylene triamine pentaacetic acid (DTPA)-extractable nickel contents of the western Anatolian serpentine soils and their vegetative contents were studied to find the possible relationships between the phytoavailable Ni amount in the soil and the Ni content of potential accumulator plants. Over half of the surface area of Turkey was targeted in the study. Aboveground parts of 413 herbaceous plants and the surface soil (0-15 cm) of 192 serpentine samples were collected. A digital elevation model and ANUSPLIN and ArcGIS 8.1 software packages were employed for generation of climatic surfaces and analysis in preparation of comparative maps. Scientifically approved Ni hyperaccumulator plant taxa as well as readily emerging species were tested under greenhouse and climate chamber conditions. The varying magnitude of nickel determined in the aboveground parts of the test plants indicated that the resistance or vulnerability and Ni requirements of a plant species were species-specific and were more effective than the Ni amount in the soil on the uptake of the element. Significant differences were found between the amount of DTPA-extractable Ni in the soil and the Ni content of hyperaccumulator Brassicaceae plants grown in the same soil bodies. Isatis pinnatiloba, which is endemic to Turkey, was introduced as a nickel hyperaccumulator species. Bottlenecks and drawbacks of phytoremediation techniques for commercial use were discussed.

Nickel hyperaccumulation by natural plants in Turkish serpentine soils

Natural plants in Turkish serpentine soils were surveyed to determine their Ni accumulation capability. Geographic distribution and diethylene triamine pentaacetic acid (DTPA)-extractable nickel contents of the western Anatolian serpentine soils and their vegetative contents were studied to find the possible relationships between the phytoavailable Ni amount in the soil and the Ni content of potential accumulator plants. Over half of the surface area of Turkey was targeted in the study. Aboveground parts of 413 herbaceous plants and the surface soil (0-15 cm) of 192 serpentine samples were collected. A digital elevation model and ANUSPLIN and ArcGIS 8.1 software packages were employed for generation of climatic surfaces and analysis in preparation of comparative maps. Scientifically approved Ni hyperaccumulator plant taxa as well as readily emerging species were tested under greenhouse and climate chamber conditions. The varying magnitude of nickel determined in the aboveground parts of the test plants indicated that the resistance or vulnerability and Ni requirements of a plant species were species-specific and were more effective than the Ni amount in the soil on the uptake of the element. Significant differences were found between the amount of DTPA-extractable Ni in the soil and the Ni content of hyperaccumulator Brassicaceae plants grown in the same soil bodies. Isatis pinnatiloba, which is endemic to Turkey, was introduced as a nickel hyperaccumulator species. Bottlenecks and drawbacks of phytoremediation techniques for commercial use were discussed.

___

  • Adriano DC, Wenzel WW, Vangronsveld J & Bolan NS (2004). Role of assisted natural remediation in environmental cleanup. Geoderma 122: 121-142.
  • Baker AJM & Brooks RR (1989). Terrestrial higher plants which hyperaccumulate metallic elements - a review of their distribution, ecology and phytochemistry. Biorecovery 1: 81- 126.
  • Baker AJM, McGrath SP, Reeves RD & Smith JAC (2000). Metal hyperaccumulator plants: a review of the ecology and physiology of a biochemical resource for phytoremediation of metal-polluted soils. In: Terry N, Banuelos GS (eds.) Phytoremediation of Contaminated Soil and Water, pp. 85-107. Boca Raton, FL: Lewis Publishers.
  • Baker AJM & Proctor J (1990). Th e infl uence of cadmium, copper, lead, and zinc on the distribution and evolution of metallophytes in the British Isles. Plant Systematics and Evolution Evol 173: 91-108.
  • Baker AJM & Whiting SN (2002). In search of the Holy Grail - a further step in understanding metal hyperaccumulation? New Phytologist 155: 1-4.
  • Boyd RS, Jaff ré T & Odom JW (1999). Variation in nickel content in the nickel-hyperaccumulating shrub Psychotria douarrei (Rubiaceae) from New Caledonia. Biotropica 31: 403-410.
  • Branquinho C, Serrano HC, Pinto MJ & Martins-Loução MA (2007). Revisiting the plant hyperaccumulation criteria to rare plants and earth abundant elements. Environmental Pollution 146: 437-443.
  • Brooks RR, Morrison RS, Reeves RD, Dudley TR & Akman Y (1979). Hyperaccumulation of nickel by Alyssum linnaeus (Cruciferae). Proceedings of the Royal Society B: Biological Sciences 203: 387- 403.
  • Chaney RL (1983). Plant uptake of inorganic waste constitutes In: Parr JF, Marsh PB & Kla JM (eds.) Land Treatment of Hazardous Wastes, pp. 50-76. Park Ridge, NJ: Noyes Data Corporation.
  • Davis PH (ed.) (1965-1985). Flora of Turkey and the East Aegean Islands. Vols. 1-9. Edinburgh: Edinburgh University Press.
  • Davis PH & Heywood VH (1973). Principles of Angiosperm Taxonomy. New York: Robert E. Kieger Publishing Co.
  • Davis PH, Mill RR & Tan K (1988). Flora of Turkey and the East Aegean Islands (Suppl. 1), Vol. 10. Edinburgh: Edinburgh University Press.
  • Ghaderian SM, Mohtadi A, Rahiminejad MR & Baker AJM (2007). Nickel and other metal uptake and accumulation by species of Alyssum (Brassicaceae) from the ultramafi cs of Iran. Environ Pollut 145: 293-298.
  • Golightly JP (1981). Nickeliferous laterite deposits. Econ Geol 75: 710-735.
  • Haq AU, Bates TE & Soon YK (1980). Comparison of extractants for plant-available zinc, cadmium, nickel, and copper in contaminated soils. Soil Sciences Society of America Journal 44: 772-777.
  • Holmgren PK, Holmgren NH & Barnett LC (eds.) (1990). Index Herbariorum. Part I: Th e Herbaria of the World. Vol. 120. New York: New York Botanical Garden.
  • Hutchinson MF (1991). Th e application of thin plate smoothing splines to continent-wide data assimilation. In: Jasper JD (ed.) BMRC Research Report No. 27, Data Assimilation Systems, pp. 104-113. Melbourne: Bureau of Meteorology.
  • Kalra YP & Maynard DG (1998). Microwave digestion of plant tissue in an open vessel. In: Kalra YP (ed.) Handbook of Reference Methods for Plant Analysis, pp. 63-67. Boca Raton, FL: CRC Press.
  • Kirkham MB (2006). Cadmium in plants on polluted soils: eff ects of soil factors, hyperaccumulation, and amendments. Geoderma 137: 19-32.
  • Leita L, De Nobili M, Mondini C, Muhlbachova G, Marchiol L, Bragato G & Contin M (1999). Infl uence of inorganic and organic fertilization on soil microbial biomass, metabolic quotient and heavy metal bioavailability. Biology and Fertility of Soils 28: 371-376.
  • Li YM, Chaney R, Brewer E, Roseberg R, Angle JS, Baker A, Reeves RD & Nelkin J (2003). Development of a technology for commercial phytoextraction of nickel: economic and technical considerations. Plant and Soil 249: 107-115.
  • Lindsay WL & Norvell WA (1978). Development of a DTPA soil test for zinc, iron, manganese and copper. Soil Sciences Society of America Journal 42: 421-428.
  • Miller OR (1998). Nitric perchloric acid wet digestion in an open vessel. In: Kalra YP (ed.) Handbook of Reference Methods for Plant Analysis, pp. 57-59. Boca Raton, FL: CRC Press.
  • Misra SG & Pande P (1974).Evaluation of a suitable extractant for available nickel in soils. Plant and Soil 41: 697-700.
  • Mutlu B (2010). New morphological characters for some Erysimum (Brassicaceae) species. Turkish Journal of Botany 34: 115-121.
  • Özhatay FN, Kültür Ş & Gürdal MB (2011). Check-list of additional taxa to the supplement Flora of Turkey V. Turkish Journal of Botany 35: 589-624.
  • Özhatay N, Kültür Ş & Aslan S (2009). Check-list of additional taxa to the supplement Flora of Turkey IV. Turkish Journal of Botany 33: 191-226.
  • Pollard AJ, Powell KD, Harper FA & Smith JAC (2002). Th e genetic basis of metal hyperaccumulation in plants. Critical Reviews in Plant Sciences 21: 539-566.
  • Reeves RD (2006). Hyperaccumulation of trace elements by plants. In: Morel JL, Echevarria G & Goncharova N (eds.) NATO Science Series. Earth and Environmental Sciences, p. 345. Dordrecht: Springer.
  • Reeves RD & Adıgüzel N (2008). Th e nickel hyperaccumulating plants of the serpentines of Turkey and adjacent areas: a review with new data. Turkish Journal of Biology 32: 143-153.
  • Reeves RD, Adıgüzel N & Baker AJM (2009). Nickel hyperaccumulation in Bornmuellera kiyakii Aytaç & Aksoy and associated plants of the Brassicaceae from Kızıldağ (Derebucak, Konya-Turkey). Turkish Journal of Botany t 33: 33-40.
  • Reeves RD & Baker AJM (2000). Metal-accumulating plants. In: Raskin I & Ensley BD (eds.) Phytoremediation of Toxic Metals: Using Plants to Clean up the Environment, pp. 193-229. New York: John Wiley & Sons.
  • Reeves RD, Kruckeberg AR, Adıgüzel N & Krämer U (2001). Studies on the fl ora of serpentine and other metalliferous areas of western Turkey. South African Journal of Sciences 97: 513-517.
  • Roosens N, Vebruggen N, Meerts P, Ximénez-Embşn P & Smith JAC (2003). Natural variation in cadmium tolerance and its relationship to metal hyperaccumulation for seven populations of Th laspi caerulescens from Western Europe. Plant Cell and Environment 26: 1657-1672.
  • Schellmann W (1983). Geochemical principles of lateritic nickel ore formation. In: Melfi AJ & Carvalho A (eds.) Proceedings of the 2nd International Seminar on Lateritisation Processes, pp. 119- 135. Sao Paulo.
  • Seregin IV & Kozhevnikova AD (2006). Physiological role of nickel and its toxic eff ects on higher plants. Russian Journal of Plant Physiology 53: 257-277.
  • Tunçay T, Uğurlu A, Kesim A, Erdoğan E, Erpul G & Bayramin İ (2006). Using geographic information systems to generate Turkey Climate Classifi cation Map. In: Proceedings of 18th International Soil Meeting on Soils Sustaining Life on Earth, Managing Soil and Technology, pp. 346-355. Şanlıurfa.
  • Ure AM (1996). Single extraction schemes for soil analysis and related applications. Th e Science of the Total Environment 78: 3-10.
  • Wang XP, Shan XQ, Zhang SZ & Wen B (2004). A model for evaluation of the phytoavailability of trace elements to vegetables under the fi eld conditions. Chemosphere 55: 811-822.
  • Zhang L, Angle JS & Chaney RL (2007). Do high-nickel leaves shed by the nickel hyperaccumulator Alyssum murale inhibit seed germination of competing plants? New Phytologist 173: 509- 516.