Marianna Bandiera

Biochar addition to an arsenic contaminated soil increases arsenic concentrations in the pore water but reduces uptake to tomato plants (Solanum lycopersicum L.).

Arsenic (As) concentrations in soil, soil pore water and plant tissues were evaluated in a pot experiment following the transplantation of tomato (Solanum lycopersicum L.) plantlets to a heavily As contaminated mine soil (~6000 mg kg(-1) pseudo-total As) receiving an orchard prune residue biochar amendment, with and without NPK fertiliser. An in-vitro test was also performed to establish if tomato seeds were able to germinate in various proportions of biochar added to nutrient solution (MS). Biochar significantly increased arsenic concentrations in pore water (500 μg L(-1)-2000 μg L(-1)) whilst root and shoot concentrations were significantly reduced compared to the control without biochar. Fruit As concentrations were very low (<3 μg kg(-1)), indicating minimal toxicity and transfer risk. Fertilisation was required to significantly increase plant biomass above the control after biochar addition whilst plants transplanted to biochar only were heavily stunted and chlorotic. Given that increasing the amount of biochar added to nutrient solution in-vitro reduced seed germination by up to 40%, a lack of balanced nutrient provision from biochar could be concluded. In summary, solubility and mobility of As were increased by biochar addition to this soil, but uptake to plant was reduced, and toxicity-transfer risk was negligible. Therefore leaching rather than food chain transfer appears the most probable immediate consequence of biochar addition to As contaminated soils.

Phytoremediation trials on metal- and arsenic-contaminated pyrite wastes (Torviscosa, Italy).

At a site in Udine, Italy, a 0.7m layer of As, Co, Cu, Pb and Zn contaminated wastes derived from mineral roasting for sulphur extraction had been covered with an unpolluted 0.15m layer of gravelly soil. This study investigates whether woody biomass phytoremediation is a realistic management option. Comparing ploughing and subsoiling (0.35m depth), the growth of Populus and Salix and trace element uptake were investigated in both pot and field trials. Species differences were marginal and species selection was not critical. Impaired above-ground productivity and low translocation of trace elements showed that bioavailable contaminant stripping was not feasible. The most significant finding was of coarse and fine roots proliferation in surface layers that provided a significant sink for trace elements. We conclude that phytostabilisation and effective immobilisation of metals and As could be achieved at the site by soil amelioration combined with woody species establishment. Confidence to achieve a long-term and sustainable remediation requires a more complete quantification of root dynamics and a better understanding of rhizosphere processes.

In situ phytoremediation of arsenic- and metal-polluted pyrite waste with field crops: Effects of soil management

Sunflower, alfalfa, fodder radish and Italian ryegrass were cultivated in severely As-Cd-Co-Cu-Pb-Zn-contaminated pyrite waste discharged in the past and capped with 0.15m of unpolluted soil at Torviscosa (Italy). Plant growth and trace element uptake were compared under ploughing and subsoiling tillages (0.3m depth), the former yielding higher contamination (∼30%) in top soil. Tillage choice was not critical for phytoextraction, but subsoiling enhanced above-ground productivity, whereas ploughing increased trace element concentrations in plants. Fodder radish and sunflower had the greatest aerial biomass, and fodder radish the best trace element uptake, perhaps due to its lower root sensitivity to pollution. Above-ground removals were generally poor (maximum of 33mgm(-2) of various trace elements), with Zn (62%) and Cu (18%) as main harvested contaminants. The most significant finding was of fine roots proliferation in shallow layers that represented a huge sink for trace element phytostabilisation. It is concluded that phytoextraction is generally far from being an efficient management option in pyrite waste. Sustainable remediation requires significant improvements of the vegetation cover to stabilise the site mechanically and chemically, and provide precise quantification of root turnover.

Minirhizotrons in Modern Root Studies

In recent years, minirhizotrons have received increasing interest in field studies for characterising several biological processes, such as fine root production, root longevity, mycorrhization and parasitism, as collecting repeated video or digital images allows the fate of individual roots to be followed in time.

Assisted phytoremediation of mixed metal(loid)-polluted pyrite waste: effects of foliar and substrate IBA application on fodder radish.

Exogenous application of plant-growth promoting substances may potentially improve phytoremediation of metal-polluted substrates by increasing shoot and root growth. In a pot-based study, fodder radish (Raphanus sativus L. var. oleiformis Pers.) was grown in As-Zn-Cu-Co-Pb-contaminated pyrite waste, and treated with indolebutyric acid (IBA) either by foliar spraying (10 mgL(-1)), or by direct application of IBA to the substrate (0.1 and 1 mgkg(-1)) in association, or not, with foliar spraying. With the exception of foliar spraying, IBA reduced above-ground biomass, whilst direct application of IBA to the substrate surface reduced root biomass (-59%). Trace element concentrations were generally increased, but removals (mg per plant) greatly reduced with IBA application, together with greater metal leaching from the substrate. It is concluded that, in our case, IBA had a negative effect on plant growth and phytoextraction of trace elements, possibly due to unsuitable root indoleacetic acid concentration following soil IBA application, the direct chelating effect of IBA and the low microbial activity in the pyrite waste affecting its breakdown.

Phytotoxicity and metal leaching in EDDS-assisted phytoextraction from pyrite wastes with Ethiopian mustard and fodder radish.

Abstract This study examines the influence of a low‐persistent chelator, [S,S]‐EDDS (ethylene diamine disuccinic acid), on the growth of Ethiopian mustard (Brassica carinata A. Braun) and fodder radish (Raphanus sativus L. var. oleiformis) and on metal leaching (ML) in As–Co–Cu–Pb–Zn‐contaminated pyrite wastes. Plants were grown in pots for 75 days with test doses of 2.5 and 5 mmol EDDS per kg of soil applied through irrigation one week before harvest, and 1 mmol EDDS per kg of soil repeated five times at 5‐ and 10‐day intervals, in comparison with untreated controls. Fodder radish treated with 1 mmol at the five‐day interval was also irrigated with 1 mg IBA (indole‐3‐butyric acid) per kg of soil every 10 days. Shoot biomass, leaf area and root growth were generally reduced by EDDS in both species, particularly in repeated applications and in radish, regardless of IBA supply, with root biomass being more affected than length and electrical capacitance (EC). EDDS generally improved shoot concentrations of Cu, Co, Zn and Pb, but repeated treatments caused significant ML (mainly of Cu), explained by a multivariate relationship (R 2 = 0.52) including the integral over time of both leaf area (R 2 = 0.43) and root EC (R 2 = 0.09). We conclude that roots play a secondary role in preventing ML, because of the prevailing effect of leaf transpiration in controlling percolation. The best metal phytoextraction was achieved with EDDS applied at harvest – a safe ML strategy, especially at the low dose of 2.5 mmol per kg of soil. Abbreviations: DTPA, diethylene triamine pentaacetic acid; EC, electrical capacitance; EDDS, ethylene diamine disuccinic acid; EDTA, ethylene diamine tetraacetic acid; HM, heavy metals; IAA, indoleacetic acid; IBA, indolebutyric acid; ICP‐OES, inductively coupled plasma optical emission spectroscopy; LA, leaf area; ML, metal leaching

A Multi-disciplinary Challenge for Phytoremediation of Metal-Polluted Pyrite Waste

Phytomanagement of metal-polluted land is receiving increasing attention as an alternative to physical and chemical methods of decontamination. Great concern focuses on metal-contaminated industrial waste or sediments, the unusual compositions of which may further limit plant establishment and growth. In this study, we focused attention on a particular industrial waste made of pyrite cinders with high levels of As, Cd, Co, Cu, Pb and Zn, which had been covered in the past with 0.15 m of unpolluted gravelly soil, later colonised by sparse spontaneous vegetation. In these conditions, on-site phytoextraction with field crops and Salicaceae woody species was rarely efficient, except for Zn, Cu and Mn. Although the estimated remediation time was extremely long, even for removing the metal-bioavailable fraction, phytomanagement can stabilise waste against wind erosion and metal movements. Poor above-ground productivity was the main factor constraining phytoextraction. Among a few crops, a maximum of 0.33 kg of metals per hectare was accumulated in the harvestable biomass of fodder radish, whereas a great stock of metals was found at root level, especially in coarse roots of Populus and Salix, suggesting the opportunity of exploiting in planta root stabilisation. For suitable cultivation of the site and to favour root growth, we recommend limiting top soil/waste mixing (shallow soil capping) and paying particular attention to species choice, fertilisation and drainage/irrigation.