Screening willow clones for Radiocesium uptake at varying potassium supply in solution culture

Transfer of radiocesium from soils to the wood of willows is generally low. Therefore, willow short rotation coppice for energy production is a possible alternative land use in areas contaminated by radiocesium. A large number of willow clones are available differing in, for example, biomass production or nutrient uptake. In order to select a clone with a high biomass production and a low radiocesium uptake, 12 clones were screened in nutrient solutions, spiked with ¹³⁴Cs. Radiocesium concentrations in the plants varied less than twofold between the clones. Shoot radiocesium concentrations were significantly related to shoot potassium concentrations (R² = 0.55).

In a second experiment, four of these clones were grown in solution culture at varying K concentrations (0.08 to 2 mM). The radiocesium uptake was more affected by K supply than by the type of clone. The shoot radiocesium concentrations were reduced between 3.5‐ and 5.2‐fold by increasing the K supply from 0.08 to 0.4 mM, A further increase to 2 vaM did not affect radiocesium uptake. We conclude that intervarietal differences between willow clones were of less significance in determining radiocesium concentrations in the shoots than the impact of external K concentrations.     

A Novel Technique for the Reattachment of Large Coral Reef Sponges

Sponges are dominant components of coral reef ecosystems, often exceeding reef-building corals in abundance. Large sponges, often more than 1 m in diameter, may be hundreds to thousands of years old. When damaged or dislodged, large sponges usually die because they are unable to reattach to the reef substratum. Because suitable methods for reattaching dislodged sponges are lacking, they are typically excluded from coral reef restoration efforts. Here we present a novel technique for the reattachment of large sponges that was tested using the Caribbean Giant barrel sponge, Xestospongia muta . Transplants of X. muta were conducted at 15- and 30-m depth off Key Largo, Florida. Despite the active hurricane season of 2005, 90% of deep and 35% of shallow transplants survived, with nearly 80% reattaching to the substratum and growing after 2.3–3 years. This technique may be generally adapted for securing large sponges in coral reef restoration efforts.     

Contrasting Effects of Farmyard Manure (FYM) and Compost for Remediation of Metal Contaminated Soil

We investigated effect of farm yard manure (FYM) and compost applied to metal contaminated soil at rate of 1% (FYM-1, compost-1), 2% (FYM-2, compost-2), and 3% (FYM-3, compost-3). FYM significantly (P < 0.001) increased dry weights of shoots and roots while compost increased root dry weight compared to control. Amendments significantly increased nickel (Ni) in shoots and roots of maize except compost applied at 1%. FYM-3 and -1 caused maximum Ni in shoots (11.42 mg kg^?1) and roots (80.92 mg kg^?1), respectively while compost-2 caused maximum Ni (14.08 mg kg^?1) and (163.87 mg kg^?1) in shoots and roots, respectively. Plants grown in pots amended with FYM-2 and compost-1 contained minimum Cu (30.12 and 30.11 mg kg^?1) in shoots, respectively. FYM-2 and compost-2 caused minimum zinc (Zn) (59.08 and 66.0 mg kg^?1) in maize shoots, respectively. FYM-2 caused minimum Mn in maize shoots while compost increased Mn in shoots and roots compared to control. FYM and compost increased the ammonium bicarbonate diethylene triamine penta acetic acid (AB-DTPA) extractable Ni and Mn in the soil and decreased Cu and Zn. Lower remediation factors for all metals with compost indicated that compost was effective to stabilize the metals in soil compared to FYM.     

Quantification of Heavy Metals in Mining Affected Soil and Their Bioaccumulation in Native Plant Species

Several anthropogenic and natural sources are considered as the primary sources of toxic metals in the environment. The current study investigates the level of heavy metals contamination in the flora associated with serpentine soil along the Mafic and Ultramafic rocks northern-Pakistan. Soil and wild native plant species were collected from chromites mining affected areas and analyzed for heavy metals (Cr, Ni, Fe, Mn, Co, Cu and Zn) using atomic absorption spectrometer (AAS-PEA-700). The heavy metal concentrations were significantly (p < 0.01) higher in mine affected soil as compared to reference soil, however Cr and Ni exceeded maximum allowable limit (250 and 60 mg kg^?1, respectively) set by SEPA for soil. Inter-metal correlations between soil, roots and shoots showed that the sources of contamination of heavy metals were mainly associated with chromites mining. All the plant species accumulated significantly higher concentrations of heavy metals as compared to reference plant. The open dumping of mine wastes can create serious problems (food crops and drinking water contamination with heavy metals) for local community of the study area. The native wild plant species (Nepeta cataria, Impatiens bicolor royle, Tegetis minuta) growing on mining affected sites may be used for soil reclamation contaminated with heavy metals.     

Do plants modulate biomass allocation in response to petroleum pollution?

Biomass allocation is an important plant trait that responds plastically to environmental heterogeneities. However, the effects on this trait of pollutants owing to human activities remain largely unknown. In this study, we investigated the response of biomass allocation of Phragmites australis to petroleum pollution by a ¹³CO₂ pulse-labelling technique. Our data show that plant biomass significantly decreased under petroleum pollution, but the root–shoot ratio for both plant biomass and ¹³C increased with increasing petroleum concentration, suggesting that plants could increase biomass allocation to roots in petroleum-polluted soil. Furthermore, assimilated ¹³C was found to be significantly higher in soil, microbial biomass and soil respiration after soils were polluted by petroleum. These results suggested that the carbon released from roots is rapidly turned over by soil microbes under petroleum pollution. This study found that plants can modulate biomass allocation in response to petroleum pollution.     

陡坡无土排岩场植被生态修复技术

针对无土陡坡排岩场特殊的立地条件,以城市污泥、粉煤灰等固体废弃物配制的人工土壤进行基质改良的基础上,以坑植式种植刺槐(Robina pseudoacacia)及棉槐(Amor-pha fruticosa),同时在种植坑中撒播牧草以培肥土壤,促进乔木生长固坡。结果表明,在人工土壤Ⅱ(粉煤灰∶城市污泥=1∶1)上种植的刺槐有较好的成活率(70%)和生长势,说明该修复技术在实现以废治废,变废为宝的同时,既解决了矿山废弃地修复中珍贵的土源问题,又改善了矿区生态环境。     

小叶白蜡接种外生菌根真菌对土壤石油烃的降解效果

采用盆栽实验研究了小叶白蜡(Fraxinus sogdiana)接种4种外生菌根真菌(E1-毛边滑锈伞(Hebeloma mesophaeusm)、E2-劣味乳菇(Lactarius insulsns)、E3-松塔牛肝菌(Stro-bilomyces floccopus)和E4-丝膜菌(Cortinarius russus)对沈抚灌区土壤石油烃的降解效果。结果表明:在白蜡不同组合双接种及混合接种中,以混合接种对土壤石油烃的降解效果最好,降解率比对照提高23.6%;其次为双接种中的E1E3和E2E4组合,降解率分别比对照提高21.0%和12.7%。接种外生菌根真菌可促进白蜡生长,尤其可明显提高其根生物量,增加侧根数,接种E1E3、E2E4和混合菌使白蜡侧根数分别增加了100%、67%和81%。相关分析表明,石油烃降解率与白蜡的侧根数呈显著相关,可能是其降解率提高的主要原因。     

越鞠丸石油醚提取物的气相色谱-质谱分析

采用气相色谱-质谱联用技术对中药复方越鞠丸石油醚提取物中的成分进行鉴定,共鉴定出60种成分,并采用峰面积归一化法确定了各成分的相对含量。     

Bioremediation of HCH present in soil by the white-rot fungus Bjerkandera adusta in a slurry batch bioreactor

In the soil remediation process, the hydrophobic characteristics of pollutants and their affinity for soil matrix may be responsible for mass transfer limitations. The degradation of hexachlorocyclohexane (HCH) isomers present in a spiked soil by the white-rot Bjerkandera adusta was evaluated in a slurry system. Experiments in shaken flasks were performed to evaluate the action of the endogenous microflora, the adsorption of HCH on the fungal biomass and the potential synergic or antagonic actions between the microflora and the fungal biomass. The fungus significantly degraded the HCH isomers from the soil slurry in the following order: α≈γ>δ>β-HCH. The degradation process was further scaled in a 5-l reactor, where the solid load and concentration of the pollutant in the soil were evaluated. At optimal conditions, 100 g soil l⁻¹ and 100 mg total HCH l⁻¹, maximal degradations of 94.5%, 78.5% and 66.1% were attained after 30 d for γ-, α- and δ-HCH isomers, respectively, representing between 1.7 and 3.1-fold the values obtained at small scale. These results indicate that minimising mass transfer resistances is a key factor for HCH degradation from soil.