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Ground Water Issue Phytoremediation of Contaminated ... - CLU-IN

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28<br />

Table 2. continued<br />

CONTAM<strong>IN</strong>ANT MEDIUM PROCESS CONCENTRATION 1<br />

Boron <strong>Water</strong> (soil<br />

solution)<br />

Perchlorate <strong>Water</strong><br />

(hydroponic<br />

solution)<br />

Radionuclides<br />

PLANT 2<br />

RESULTS/NOTES<br />

Phytoextraction 10 mg water-extractable B/L Indian mustard (Brassica juncea Czern<br />

L.), tall fescue (Festuca arundinacea<br />

Schreb. L.), birdsfoot trefoil (Lotus<br />

corniculatus L.), kenaf (Hibiscus<br />

cannibinus L.)<br />

Phytoextraction<br />

Phytodegradation<br />

Rhizodegradation<br />

Bañuelos, 1996<br />

REFERENCE<br />

Mean B concentrations in shoots ranged from 122 mg B/kg dry matter in birdsfoot trefoil to 879 mg B/kg dry matter in kenaf<br />

leaves. In two years, each plant species lowered extractable B concentrations in soil by at least 25%.<br />

10, 22, 100 mg/L Willow (Salix nigra), Eastern cottonwood<br />

(Populus deltoides and hybrid populus),<br />

and eucalyptus (Eucalyptus cineria).<br />

Nzengung et al., 1999<br />

Willows had best growth under hydroponic conditions and degraded perchlorate from 10 mg/L to below detection (2 g/L) in<br />

about 20 days, from 22 mg/L to BD in about 35 days, and from 100 mg/L to BD in about 53 days. 1.3% <strong>of</strong> initial perchlorate<br />

mass was found in willow plant tissues, especially leaves and upper stems (branches). Leaves had 813.1 mg/kg perchlorates.<br />

Some evidence for perchlorate degradation within leaves. Perchlorate degradation rates decreased as nitrate concentration<br />

increased, and type <strong>of</strong> nitrogen source affects perchlorate degradation rate.<br />

Cesium or 137 Cs Soil Phytoextraction 2600 Bq/kg average Amaranth species Dushenkov et al., 1999<br />

Eu(III)<br />

[surrogate for<br />

radionuclide<br />

Am(III)]<br />

<strong>Water</strong> Rhiz<strong>of</strong>iltration<br />

Rhiz<strong>of</strong>iltration<br />

Extraction <strong>of</strong> 137 Cs was limited by binding to soil; addition <strong>of</strong> amendments did not increase bioavailability.<br />

C o = 200 g/L Sunflowers Dushenkov et al., 1997<br />

In bench-scale and pilot-scale engineered systems using the stable isotope, C o decreased noticeably after 6 hours, then went<br />

below 3 g/L after 24 hours.<br />

20 to 2000 g/L Indian mustard Salt et al., 1997<br />

Accumulation by the roots, with bioaccumulation coefficients <strong>of</strong> 100 to 250.<br />

<strong>Water</strong> Rhiz<strong>of</strong>iltration 3.3 x 10 -4 M (50 mg/L) <strong>Water</strong> hyacinth (Eichhornia crassipes) Kelley et al., 1999<br />

26% <strong>of</strong> the Eu(III) in solution was removed. Eu(III) on roots was 0.01 g/g dry weight root material. Almost all <strong>of</strong> the<br />

removed Eu(III) was found on the roots.<br />

60 Co Soil Phytoextraction Co = 1.59 Bq 60 Co/g soil Yellow sweetclover (Melilotus <strong>of</strong>ficinalis<br />

(L.) Lam) and Sudan grass (Sorghum<br />

sudanese (Piper) Stapf.)<br />

Rogers and Williams, 1986<br />

2.6% <strong>of</strong> the total 60 Co in soil was removed by two harvests <strong>of</strong> clover, at 65 and 93 days. 1.2% <strong>of</strong> the total 60 Co in soil was<br />

removed by two harvests <strong>of</strong> grass, at 85 and 119 days.

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