16 rhizofiltration

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    RHIZOFILTRATION

    Rhizofiltration is primarily used to

    remediate extractedgroundwater, surface water, and

    waste water with low

    contaminant concentrations.

    Rhizofiltration defined as the use ofplants, both terrestrial and

    aquatic, to absorb, concentrate,

    and precipitate contaminants

    from polluted aqueous sources in

    their roots.

    Rhizofiltration can be used for Pb,

    Cd, Cu, Ni, Zn, and Cr, which are

    primarily retained within the roots

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    RHIZOFILTRATIONRhizofiltration dikenal juga dengan nama Hydroponic System.

    Process goal-nya juga termasuk kategori remediation.

    Medianya, pumped or surficial water stream.

    Mechanism-nya phytostabilization, phytoaccumulation, evapotranspiration.

    Typical contaminant berupa metal dan juga radionucleid.

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    Rhizofiltration

    Rhizofiltration pada intinya adalah memindahkan kontaminandari air dan aliran limbah cair (run of fpertanian, industr ia ldischarges, nuc lear mater ia l processing).

    Figure. Flow through rhizofiltrationsystem. The system contains 8-12 weeks-old sunflower plantswith roots immersed in flowingcontaminated water.

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    Rhizofiltration

    Mekanisme Adsorpsi dan Absorbsi oleh akar tanaman memegang peran

    penting dalam rhizofiltrasi ; dan akar dengan luas permukaan yang luaslebih dianjurkan.

    Terrestrial plant are preferred because they have a fibrous and much

    longer root system, increasing the amount of root area.

    Sunflower, indian mustard, tobacco, rye, spinach and corn have been

    studied for their ability to remove lead from water, with sunflower

    having the greatest ability.

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    Beberapa aplikasi Rhizofiltration

    Epcot Center, suatu sistem tertutup dengan cara re-

    circulating nutrients telah dikenalkan sebagai salah satu

    kegiatan rhizofiltrasi yang digabungkan dengan biofiltrasi

    menggunakan beberapa spesies tertentu (Negri and

    Hinchman, 1996).

    Rhizofiltrasi juga diterapkan di San Fransisco Bay ;

    bekerjasama dengan Chevron membangun sebuah

    wetland constructions yang mampu memindahkan hampir89% Se yang mengkontaminasi perairan tersebut dari

    kegiatan industri oil refinery.

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    Rhizofiltration The water f lowin g into the wetland was measured to have 20-

    30 g/lt Se, while the ou tf low fr om the wetland had less than 5

    g/lt (Hans en et al., 1998).

    Pada studi di San Joaquin Valley (Gao et al., 2003), a flowthrough wet land sy stem was con structed with cells conta in ing

    either a single species, or a combinat ion o f species

    [Schoenoplectus robus tus, Juncu s balt icus, Spartina

    alterni f lora, Polypogon monspel l iensis , Dist ichl is sp icata,

    Thypa lati fol ia, and Ruppia marit ima].

    Four years after plant ing , com prehensive analysis showed that

    59% of the Se remained in the wetland, mostly in the organic

    detr i tal layer and surface sediment, 35% in the outf low, 4% in

    the seepage and 2% to vo lati l ization.

    Menunjukkan bahwa wetland plant uptake of Se varies with species type dantumbuhan yang berwarna biru diatas adalah tumbuhan pada skala percobaan yangberpotensi melakukan high uptake Se (Gao et al., 2003).

    Beberapa aplikasi Rhizofiltration

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    Rhizofiltration

    Gambar diatas menunjukkan suatu mekanisme sederhana rhizofiltrasidengan menggunakan spesies tumbuhan pada suatu kolam buatanuntuk menurunkan tingkat akumulasi logam berat Hydroponicsystem.

    The cost of remediation by rhizofiltration has been estimated to be $2-6 per 1000 gallons of water.

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    Penelitian di Indonesia (1)

    Rhizofiltrasi kromium dan keragaman komunitas rhizobakteri pada

    tanaman air (Anna Safarrida S2 program)

    Tujuan : mengetahui ketahanan dan serapan tanaman air

    terhadap Cr ; keragaman komunitas rhizobakteri tanaman air

    yang dipapar Cr ; dan isolasi identifikasi rhizobakteri yang

    tahan Cr.

    Menggunakan 4 tanaman (Pistia stratiotes, Eichornia crassipes,

    Lemna minor, dan Salvinia minor) ditumbuhkan pd medium

    buatan (Hoagland) yang dipasok 0, 1, 2, 4 dan 8 ppm Cr.

    Selanjutnya tanaman juga diujikan lebih lanjut dlm limbah cair

    industri penyamakan kulit.

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    Penelitian di Indonesia (2)

    Kemampuan toleransi dan serapan tan thd Cr didasarkan pd

    pengamatan morfologi dan analisis kadar Cr dlm biomass.

    Keragaman komunitas rhizobakteri dianalisis mell pendekatan

    culture independent dan dependent ; koloni2 yg berbeda pd

    culture dependent diseleksi ketahanannya thd Cr dan dianalisis

    keragamannya dg Rep-PCR.

    Isolat yg terpilih diidentifikasi berdasar sekuen parsial gen 16S

    rDNA.

    P.stratiotes dan Salvinia sp. Berturut-turut mempunyai

    ketahanan dan serapan paling rendah dan paling tinggi thd Cr

    dibanding tanaman lain.

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    Penelitian di Indonesia (3)

    Pd pendekatan culture independent dan dependent, paparan Cr

    menurunkan keragaman komunitas rhizobakteri, baik pdP.stratiotes maupun Salvinia sp, dimana keragaman tertinggi

    justru di Salvinia sp.

    Hasil pengujian ketahanan thd Cr diperoleh 6 isolat

    rhizobakteri yg tahan hingga 40 ppm ; dan berhasildiidentifikasi sebagai Aeromonas sp, Rhodococcus fascians,

    Bacillus sp. Pseudomonas mosselii, Agrobacterium tumefaciens

    dan Brevibacterium sp.

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    Advantages of Rhizofiltration

    Readily absorbs metals

    The ability to use both terrestrial and aquatic plants foreither in situ or ex situ applications.

    Contaminants do not have to be translocated to theshoots.

    Species other than hyperaccumulators may be used.

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    Disadvantages of Rhizofiltration

    Applicable for treatment of water only.

    Metals are concentrated in plant biomass and must bedisposed of eventually (~there is periodic harvesting andplant disposal).

    Constant need to adjust pH.

    Plant may first need to be grown in a greenhouse ornursery.

    Tank design must be well engineered,

    Good understanding of the chemical speciation /interaction is needed.

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