ライフサイエンスコーパス: phytoremediation

1 egume herbs provides an effective way for Pb phytoremediation.

2 nts of technical installations to facilitate phytoremediation.

3 n capacity of plants as a potential route to phytoremediation.

4 t to the field of natural endophyte-assisted phytoremediation.

5 the development of improved plants for metal phytoremediation.

6 plant and one that is frequently utilized in phytoremediation.

7 owth, productivity, carbon sequestration and phytoremediation.

8 ribute to the wider and safer application of phytoremediation.

9 and heavy metals and is successfully used in phytoremediation.

10 the effectiveness of transgenic poplars for phytoremediation.

11 pNifS overexpressors show promise for use in phytoremediation.

12 toxic impacts to plants used in this type of phytoremediation.

13 wledge to enhance the capacity of plants for phytoremediation.

14 s suggests some of them as candidates for Se phytoremediation.

15 erance and of a plant's potential for use in phytoremediation.

16 may be applied in crop biofortification and phytoremediation.

17 e, providing an attractive technology for Se phytoremediation.

18 ntrations, raising concern about its use for phytoremediation.

19 and time-consuming, particularly when using phytoremediation, a long-term remedial approach.

20 As a model system for RDX phytoremediation, A. thaliana expressing xplA was grown

21 oward xenobiotics is of major importance for phytoremediation applications.

22 l not only be investigated in the context of phytoremediation but also from a clinical parasitologica

23 ork has the potential to increase the use of phytoremediation by decreasing toxicity and increasing d

24 n that will contribute to the advancement of phytoremediation by the future engineering of plants wit

25 We argue that success in phytoremediation can be hastened through understanding t

26 model plant Arabidopsis to determine whether phytoremediation can be used to clean up contaminated si

27 brane proteins could further enhance mercury phytoremediation capabilities.

28 for the creation of plants with enhanced Se phytoremediation capacity.

29 oduction of plants with superior heavy metal phytoremediation capacity.

30 f nitroreductase (NR) in plants suitable for phytoremediation could facilitate the effective cleanup

31 trategies for developing transgenic improved phytoremediation cultivars for commercial use.

32 In summary, to maximize phytoremediation efficiency of hydrophobic pollutants in

33 nderstanding of plant activities critical to phytoremediation has been achieved, but recent progress

34 Plant-based environmental remediation, or phytoremediation, has been widely pursued in recent year

35 s (a macroalga, Chara canescens) for SeCN(-) phytoremediation in upland and wetland situations, respe

36 tes the importance of microscopy methods for phytoremediation investigations.

37 Phytoremediation is a potentially low cost remediation t

38 Phytoremediation is a technique that offers an environme

39 Phytoremediation is an inexpensive and effective techniq

40 of chloroplast transformation to enhance Hg phytoremediation is particularly beneficial because it p

41 Phytoremediation is the use of plants to clean up enviro

42 A major goal of phytoremediation is to transform fast-growing plants wit

43 d inaccessible nature of contaminated areas, phytoremediation may be a viable clean-up approach.

44 ves may be an important, yet under-explored, phytoremediation mechanism.

45 leaf tissue could potentially be used in the phytoremediation of any pollutant for which it is possib

46 ne the potential impact of photolysis on the phytoremediation of contaminants.

47 ing CYP76B1 may also be a potential tool for phytoremediation of contaminated sites.

48 adaptability, especially for reclamation and phytoremediation of contaminated soils and waters.

49 e been reported in the use of plants for the phytoremediation of cyanide compounds and evidence for t

50 rass species should play a vital role in the phytoremediation of environmental arsenic contamination.

51 merA constructs may provide a means for the phytoremediation of mercury pollution.

52 ncrease crop productivity in marginal soils, phytoremediation of metal contaminated soils, and organi

53 y viable molecular genetic approaches to the phytoremediation of metal ion pollution.

54 The phytoremediation of metal-contaminated soils offers a lo

55 veloping plant species better suited for the phytoremediation of metal-contaminated soils.

56 products and foreign proteins to a model for phytoremediation of organic and metal contaminants.

57 Phytoremediation of organic pollutants, such as explosiv

58 mulator plants with increased efficiency for phytoremediation of Se-contaminated environments.

59 Indian mustard is promising for the phytoremediation of SeCN(-) -contaminated soil and water

60 ating or volatilizing plants may be used for phytoremediation of selenium pollution and as fortified

61 serve a direct degradative function for the phytoremediation of sites contaminated by organic nitrat

62 The efficacy of transgenic plants in the phytoremediation of small organic contaminants has been

63 um has particular relevance to PGPB enhanced phytoremediation of soils contaminated through mining an

64 A limitation to phytoremediation of solvents has been toxicity of the co

65 e on the influence of endophytic bacteria on phytoremediation of widespread environmental contaminant

66 three-year field trial of endophyte-assisted phytoremediation on the Middlefield-Ellis-Whisman Superf

67 cystin-LR, remove it from the environment by phytoremediation, or enhance yields in crops exposed to

68 forestry or energy plantations, reclamation, phytoremediation, or other applications.

69 veloped to evaluate the cadmium and lead ion phytoremediation potential by the floating aquatic macro

70 lities for enhancing the metal tolerance and phytoremediation potential of higher plants via expressi

71 from a hyperaccumulator in order to increase phytoremediation potential.

72 ble trait for the development of a practical phytoremediation processes for removal of this potential

73 Promising phytoremediation research using transgenic model plant s

74 sess the significance of these pathways from phytoremediation sites at Travis and Fairchild Air Force

75 latilization of TCE and similar compounds at phytoremediation sites.

76 nobiotic compound, which should help improve phytoremediation strategies directed at TNT and other ni

77 vity could contribute towards development of phytoremediation strategies to clean up TNT from pollute

78 We have developed a genetics-based phytoremediation strategy for arsenic in which the oxyan

79 ssential for the development of an efficient phytoremediation strategy for this element.

80 Most phytoremediation studies utilize merA or merB genes to m

81 stress tolerance strategies in a real-world phytoremediation system.

82 mineralization has relevant implications for phytoremediation techniques and for further biotechnolog

83 cal and environmentally friendly approach to phytoremediation techniques, but analytical methods for

84 A real-world biological application of phytoremediation, the field growth of 10 Salix cultivars

85 Phytoremediation, the use of plants for remediation of s

86 Phytoremediation uses plants to remove pollutants from t

87 and the presence of legume or grass herbs on phytoremediation with a legume tree, Robinia pseudoacaci

88 , particularly in the rhizosphere, providing phytoremediation with a solid mechanistic understanding.

89 ely, especially when recycling of ashes from phytoremediation wood through application in agriculture

90 The phytoremediation wood was harvested from a TE-contaminat