Hyperaccumulators table – 3
This list covers hyperaccumulators, plant species which accumulate, or are tolerant of, radionuclides, hydrocarbons and organic solvents, and inorganic compounds.
See also:
- Hyperaccumulators table – 1 : Ag, Al, As, Be, Cr, Cu, Hg, Mn, Mo, Naphthalene, Pb, Pd, Se, Zn
- Hyperaccumulators table – 2 : Nickel
| Contaminant | Accumulation rates | Latin name | English name | H-Hyperaccumulator or A-Accumulator P-Precipitator T-Tolerant | Notes | Sources | ||
| Cd | Athyrium yokoscense | Cd, Cu, Pb, Zn | Origin Japan | |||||
| Cd | >100 | Avena strigosa Schreb. | New-Oat Lopsided Oat or Bristle Oat | |||||
| Cd | H- | Bacopa monnieri | Smooth Water Hyssop, Waterhyssop, Brahmi, Thyme-leafed gratiola, Water hyssop | Cr, Cu, Hg, Pb | Origin India; aquatic emergent species | |||
| Cd | Brassicaceae | Mustards, mustard flowers, crucifers or, cabbage family | Cd, Cs, Ni, Sr, Zn | Phytoextraction | ||||
| Cd | A- | Brassica juncea L. | Indian mustard | Cr, Cu, Ni, Pb, Pb, U, Zn | cultivated | |||
| Cd | H- | Vallisneria americana | Tape Grass | Cr, Cu, Pb | Origins Europe and N. Africa; extensively cultivated in the aquarium trade | |||
| Cd | >100 | Crotalaria juncea | Sunn or sunn hemp | High amounts of total soluble phenolics | ||||
| Cd | H- | Eichhornia crassipes | Water Hyacinth | Cr, Cu, Hg, Pb, Zn. Also Cs, Sr, U and pesticides | Pantropical/Subtropical, 'the troublesome weed' | |||
| Cd | Helianthus annuus | Sunflower | Phytoextraction & rhizofiltration | |||||
| Cd | H- | Hydrilla verticillata | Hydrilla | Cr, Hg, Pb | ||||
| Cd | H- | Lemna minor | Duckweed | Pb, Cu, Zn | Native to North America and widespread | |||
| Cd | T- | Pistia stratiotes | Water lettuce | Cu, Hg, Cr | Pantropical, Origin South U.S.A.; aquatic herb | |||
| Cd | Salix viminalis L. | Common Osier, Basket Willow | Ag, Cr, Hg, Se, petroleum hydrocarbons, organic solvents, MTBE, TCE and by-products; Pb, U, Zn ; Potassium ferrocyanide | Phytoextraction. Perchlorate | ||||
| Cd | Spirodela polyrhiza | Giant Duckweed | Cr, Pb, Ni, Zn | Native to North America | ||||
| Cd | >100 | Tagetes erecta L. | African-tall | Tolerance only. Lipid peroxidation level increases; activities of antioxidative enzymes such as superoxide dismutase, ascorbate peroxidase, glutathione reductase, and catalase are depressed. | ||||
| Cd | Thlaspi caerulescens | Alpine pennycress | Cr, Co, Cu, Mo, Ni, Pb, Zn | Phytoextraction. Its rhizosphere's bacterial population is less dense than with Trifolium pratense but richer in specific metal-resistant bacteria. | ||||
| Cd | 1000 | Vallisneria spiralis | Eel grass | 37 records of plants; origin India | ||||
| Cs-137 | Acer rubrum, Acer pseudoplatanus | Red maple, Sycamore maple | Pu-238, Sr-90 | Leaves: much less uptake in Larch and Sycamore maple than in Spruce. | ||||
| Cs-137 | Agrostis spp. | Agrostis spp. | Grass or Forb species capable of accumulating radionuclides | |||||
| Cs-137 | up to 3000 Bq kg-1 | Amaranthus retroflexus | Redroot Amaranth | Cd, Cs, Ni, Sr, Zn | Phytoextraction. Can accumulate radionuclides, ammonium nitrate and ammonium chloride as chelating agents. Maximum concentration is reached after 35 days of growth. | |||
| Cs-137 | Brassicaceae | Mustards, mustard flowers, crucifers or, cabbage family | Cd, Cs, Ni, Sr, Zn | Phytoextraction. Ammonium nitrate and ammonium chloride as chelating agents. | ||||
| Cs-137 | Brassica juncea | Indian mustard | Contains 2 to 3 times more Cs-137 in his roots than in the biomass above ground Ammonium nitrate and ammonium chloride as chelating agents. | |||||
| Cs-137 | Cerastium fontanum | Big Chickweed | Grass or Forb species capable of accumulating radionuclides | |||||
| Cs-137 | Beta vulgaris, Chenopodiaceae, Kail? and/or Salsola? | Beet, Quinoa, Russian thistle | Sr-90, Cs-137 | Grass or Forb species capable of accumulating radionuclides | ||||
| Cs-137 | Cocos nucifera | Coconut palm | Tree able to accumulate radionuclides | |||||
| Cs-137 | Eichhornia crassipes | Water hyacinth | U, Sr. Also Cd, Cr, Cu, Hg, Pb, Zn and pesticides. | |||||
| Cs-137 | Eragrostis bahiensis | Bahia lovegrass | Glomus mosseae as amendment. It increases the surface area of the plant roots, allowing roots to acquire more nutrients, water and therefore more available radionuclides in soil solution. | |||||
| Cs-137 | Eucalyptus tereticornis | Forest redgum | Sr-90 | Tree able to accumulate radionuclides | ||||
| Cs-137 | Festuca arundinacea | Tall fescue | Grass or Forb species capable of accumulating radionuclides | |||||
| Cs-137 | Festuca rubra | Fescue | Grass or Forb species capable of accumulating radionuclides | |||||
| Cs-137 | Glomus mosseae as chelating agent | Mycorrhizal fungi | Glomus mosseae as amendment. It increases the surface area of the plant roots, allowing roots to acquire more nutrients, water and therefore more available radionuclides in soil solution. | |||||
| Cs-137 | Glomus intradices | Mycorrhizal fungi | Glomus mosseae as chelating agent. It increases the surface area of the plant roots, allowing roots to acquire more nutrients, water and therefore more available radionuclides in soil solution. | |||||
| Cs-137 | 4900-8600 | Helianthus annuus | Sunflower | U, Sr | Accumulates up to 8 times more Cs-137 than timothy or foxtail. Contains 2 to 3 times more Cs-137 in its roots than in the biomass above ground. | |||
| Cs-137 | Larix | Larch | Leaves: much less uptake in Larch and Sycamore maple than in Spruce. 20% of the translocated caesium into new leaves resulted from root-uptake 2.5 years after the Chernobyl accident. | |||||
| Cs-137 | Liquidambar styraciflua | American Sweet Gum | Pu-238, Sr-90 | Tree able to accumulate radionuclides | ||||
| Cs-137 | Liriodendron tulipifera | Tulip tree | Pu-238, Sr-90 | Tree able to accumulate radionuclides | ||||
| Cs-137 | Lolium multiflorum | Italian Ryegrass | Sr | Mycorrhizae: accumulates much more Cs-137 and Sr-90 when grown in Sphagnum peat than in any other medium incl. Clay, sand, silt and compost. | ||||
| Cs-137 | Lolium perenne | Perennial ryegrass | Can accumulate radionuclides | |||||
| Cs-137 | Panicum virgatum | Switchgrass | ||||||
| Cs-137 | Phaseolus acutifolius | Tepary Beans | Cd, Cs, Ni, Sr, Zn | Phytoextraction. Ammonium nitrate and ammonium chloride as chelating agents | ||||
| Cs-137 | Phalaris arundinacea L. | Reed canary grass | Cd, Cs, Ni, Sr, Zn Ammonium nitrate and ammonium chloride as chelating agents. | Phytoextraction | ||||
| Cs-137 | Picea abies | Spruce | Conc. about 25-times higher in bark compared to wood, 1.5–4.7 times higher in directly contaminated twig-axes than in leaves. | |||||
| Cs-137 | Pinus radiata, Pinus ponderosa | Monterey Pine, Ponderosa pine | Sr-90. Also petroleum hydrocarbons, organic solvents, MTBE, TCE and by-products | Copper flower | 27 records of plants; origin Africa. Vernacular name: 'copper flower'. This species' phanerogamme has the highest cobalt content. Its distribution could be governed by cobalt rather than copper. | |||
| Co | H- | Thlaspi caerulescens | Alpine pennycress | Cd, Cr, Cu, Mo, Ni, Pb, Zn | Phytoextraction | |||
| Pu-238 | Acer rubrum | Red maple | Cs-137, Sr-90 | Tree able to accumulate radionuclides | ||||
| Pu-238 | Liquidambar styraciflua | American Sweet Gum | Cs-137, Sr-90 | Tree able to accumulate radionuclides | ||||
| Pu-238 | Liriodendron tulipifera | Tulip tree | Cs-137, Sr-90 | Tree able to accumulate radionuclides | ||||
| Ra | No reports found for accumulation | |||||||
| Sr | Acer rubrum | Red maple | Cs-137, Pu-238 | Tree able to accumulate radionuclides | ||||
| Sr | Brassicaceae | Mustards, mustard flowers, crucifers or, cabbage family | Cd, Cs, Ni, Zn | Phytoextraction | ||||
| Sr | Beta vulgaris, Chenopodiaceae, Kail? and/or Salsola? | Beet, Quinoa, Russian thistle | Sr-90, Cs-137 | Can accumulate radionuclides | ||||
| Sr | Eichhornia crassipes | Water Hyacinth | Cs-137, U-234, 235, 238. Also Cd, Cr, Cu, Hg, Pb, Zn and pesticides. | In pH of 9, accumulates high concentrations of Sr-90 with approx. 80 to 90% of it in its roots | ||||
| Sr | Eucalyptus tereticornis | Forest redgum | Cs-137 | Tree able to accumulate radionuclides | ||||
| Sr | H-? | Helianthus annuus | Sunflower | Accumulates radionuclides; high absorption rate. Phytoextraction & rhizofiltration | ||||
| Sr | Liquidambar styraciflua | American Sweet Gum | Cs-137, Pu-238 | Tree able to accumulate radionuclides | ||||
| Sr | Liriodendron tulipifera | Tulip tree | Cs-137, Pu-238 | Tree able to accumulate radionuclides | ||||
| Sr | Lolium multiflorum | Italian Ryegrass | Cs | Mycorrhizae: accumulates much more Cs-137 and Sr-90 when grown in Sphagnum peat than in any other medium incl. clay, sand, silt and compost. | ||||
| Sr | 1.5-4.5 % in their shoots | Pinus radiata, Pinus ponderosa | Monterey Pine, Ponderosa pine | Petroleum hydrocarbons, organic solvents, MTBE, TCE and by-products; Cs-137 | Phytocontainment. Accumulate 1.5-4.5 % of Sr-90 in their shoots. | |||
| Sr | Apiaceae | Carrot or parsley family | Species most capable of accumulating radionuclides | |||||
| Sr | Fabaceae | Legume, pea, or bean family | Species most capable of accumulating radionuclides | |||||
| U | Amaranthus | Amaranth | Cd, Cr, Cu, Ni, Pb, Pb, Zn | Citric acid chelating agent and see note. Cs: maximum concentration is reached after 35 days of growth. | ||||
| U | Brassica juncea, Brassica chinensis, Brassica narinosa | Cabbage family | Cd, Cr, Cu, Ni, Pb, Pb, Zn | Citric acid chelating agent increases uptake 1000 times, and see note | ||||
| U-234, 235, 238 | Eichhornia crassipes | Water Hyacinth | Cs-137, Sr-90. Also Cd, Cr, Cu, Hg, Pb, Zn, and pesticides. | |||||
| U-234, 235, 238 | 95% of U in 24 hours. | Helianthus annuus | Sunflower | Accumulates radionuclides; At a contaminated wastewater site in Ashtabula, Ohio, 4 wk-old splants can remove more than 95% of uranium in 24 hours. Phytoextraction & rhizofiltration. | ||||
| U | Juniperus | Juniper | Accumulates U in his roots | |||||
| U | Picea mariana | Black Spruce | Accumulates U in his twigs | |||||
| U | Quercus | Oak | Accumulates U in his roots | |||||
| U | Kail? and/or Salsola? | Russian thistle | ||||||
| U | Salix viminalis | Common Osier | Ag, Cr, Hg, Se, petroleum hydrocarbons, organic solvents, MTBE, TCE and by-products; Cd, Pb, Zn ; potassium ferrocyanide | Phytoextraction. Perchlorate | ||||
| U | Silene vulgaris | Bladder campion | ||||||
| U | Zea mays | Maize | ||||||
| U | A-? | |||||||
| Radionuclides | Tradescantia bracteata | Spiderwort | Indicator for radionuclides: the stamens become pink when exposed to radionuclides | |||||
| Benzene | Chlorophytum comosum | spider plant | ||||||
| Benzene | Ficus elastica | rubber fig, rubber bush, rubber tree, rubber plant, or Indian rubber bush | ||||||
| Benzene | Kalanchoe blossfeldiana | Kalanchoe | seems to take benzene selectively over toluene. | |||||
| Benzene | Pelargonium x domesticum | Germanium | ||||||
| BTEX | Phanerochaete chrysosporium | White rot fungus | DDT, Dieldrin, Endodulfan, Pentachloronitro-benzene, PCP | Phytostimulation | ||||
| DDT | Phanerochaete chrysosporium | White rot fungus | BTEX, Dieldrin, Endodulfan, Pentachloronitro-benzene, PCP | Phytostimulation | ||||
| Dieldrin | Phanerochaete chrysosporium | White rot fungus | DDT, BTEX, Endodulfan, Pentachloronitro-benzene, PCP | Phytostimulation | ||||
| Endosulfan | Phanerochaete chrysosporium | White rot fungus | DDT, BTEX, Dieldrin, PCP, Pentachloronitro-benzène | Phytostimulation | ||||
| Fluoranthene | Cyclotella caspia '''' | Approximate rate of biodegradation on 1st day: 35%; on 6th day: 85%. | ||||||
| Hydrocarbons | Cynodon dactylon Pers. | Bermuda grass | Mean petroleum hydrocarbons reduction of 68% after 1 year | |||||
| Hydrocarbons | Festuca arundinacea | Tall fescue | Mean petroleum hydrocarbons reduction of 62% after 1 year | |||||
| Hydrocarbons | Pinus spp. | Pine spp. | Organic solvents, MTBE, TCE and by-products. Also Cs-137, Sr-90 | Phytocontainment. Tree able to accumulate radionuclides | ||||
| Hydrocarbons | Salix spp. | Osier spp. | Ag, Cr, Hg, Se, organic solvents, MTBE, TCE and by-products; Cd, Pb, U, Zn ; Potassium ferrocyanide | Phytoextraction. Perchlorate | ||||
| MTBE | Pinus spp. | Pine spp. | Petroleum hydrocarbons, Organic solvents, TCE and by-products. Also Cs-137, Sr-90 | Phytocontainment. Tree able to accumulate radionuclides | ||||
| MTBE | Salix spp. | Osier spp. | Ag, Cr, Hg, Se, petroleum hydrocarbons, organic solvents, TCE and by-products; Cd, Pb, U, Zn ; Potassium ferrocyanide | Phytoextraction, phytocontainment. Perchlorate | ||||
| Organic solvents | Pinus spp. | Pine spp. | Petroleum hydrocarbons, MTBE, TCE and by-products. Also Cs-137, Sr-90 | Phytocontainment. Tree able to accumulate radionuclides | ||||
| Organic solvents | Salix spp. | Osier spp. | Ag, Cr, Hg, Se, petroleum hydrocarbons, MTBE, TCE and by-products; Cd, Pb, U, Zn ; Potassium ferrocyanide | Phytoextraction. phytocontainment. Perchlorate | ||||
| Organic solvents | Pinus spp. | Pine spp. | Petroleum hydrocarbons, MTBE, TCE and by-products. Also Cs-137, Sr-90 | Phytocontainment. Tree able to accumulate radionuclides | ||||
| Organic solvents | Salix spp. | Osier spp. | Ag, Cr, Hg, Se, petroleum hydrocarbons, MTBE, TCE and by-products; Cd, Pb, U, Zn ; Potassium ferrocyanide | Phytoextraction. phytocontainment. Perchlorate | ||||
| PCNB | Phanerochaete chrysosporium | White rot fungus | DDT, BTEX, Dieldrin, Endodulfan, PCP | Phytostimulation | ||||
| Potassium ferrocyanide | 8.64% to 15.67% of initial mass | Salix babylonica L. | Weeping Willow | Ag, Cr, Hg, Se, petroleum hydrocarbons, organic solvents, MTBE, TCE and by-products ; Cd, Pb, U, Zn ; Potassium ferrocyanide | Phytoextraction. Perchlorate. No ferrocyanide in air from plant transpiration. A large fraction of initial mass was metabolized during transport within the plant. | |||
| Potassium ferrocyanide | 8.64% to 15.67% of initial mass | Salix matsudana Koidz, Salix matsudana Koidz x Salix alba L. | Hankow Willow, Hybrid Willow | Ag, Cr, Hg, Se, petroleum hydrocarbons, organic solvents, MTBE, TCE and by-products ; Cd, Pb, U, Zn. | No ferrocyanide in air from plant transpiration. | |||
| PCB | Rosa spp. | Paul's Scarlet Rose | Phytodegradation | |||||
| PCP | Phanerochaete chrysosporium | White rot fungus | DDT, BTEX, Dieldrin, Endodulfan, Pentachloronitro-benzène | Phytostimulation | ||||
| TCE | Chlorophytum comosum | spider plant | Seems to lower the removal rates of benzene and methane. | |||||
| TCE and by-products | Pinus spp. | Pine spp. | Petroleum hydrocarbons, organic solvents, MTBE. Also Cs-137, Sr-90 | Phytocontainment. Tree able to accumulate radionuclides | ||||
| TCE and by-products | Salix spp. | Osier spp. | Ag, Cr, Hg, Se, petroleum hydrocarbons, organic solvents, MTBE; Cd, Pb, U, Zn ; Potassium ferrocyanide | Phytoextraction, phytocontainment. Perchlorate | ||||
| Musa (genus) | Banana tree | Extra-dense root system, good for rhizofiltration. | ||||||
| Cyperus papyrus | Papyrus | Extra-dense root system, good for rhizofiltration | ||||||
| Taros | Extra-dense root system, good for rhizofiltration | |||||||
| Brugmansia spp. | Angel's trumpet | Semi-anaerobic, good for rhizofiltration | ||||||
| Caladium | Caladium | Semi-anaerobic and resistant, good for rhizofiltration | ||||||
| Caltha palustris | Marsh marigold | Semi-anaerobic and resistant, good for rhizofiltration | ||||||
| Iris pseudacorus | Yellow Flag, paleyellow iris | Semi-anaerobic and resistant, good for rhizofiltration | ||||||
| Mentha aquatica | Water Mint | Semi-anaerobic and resistant, good for rhizofiltration | ||||||
| Scirpus lacustris | Bulrush | Semi-anaerobic and resistant, good for rhizofiltration | ||||||
| Typha latifolia | Broadleaf cattail | Semi-anaerobic and resistant, good for rhizofiltration |