Arsenate interferes with enzymatic processes and inhibits inorganic phosphorus (Pi) uptake in many plants. This study examined the role of phytase and phosphatase in arsenate tolerance and phosphorus (P) acquisition in the arsenic hyperaccumulator Pteris vittata . Enzyme-mediated hydrolysis of phytate in P. vittata extracts was not inhibited by arsenate at 5 mM or by heating at 100 °C for 10 min. Root exudates of P. vittata exhibited the highest phytase activity (18 nmol Pi mg(-1) protein min(-1)) when available P was low, allowing its growth on media amended with phytate as the sole source of P. Phosphorus concentration in P. vittata gametophyte tissue grown on phytate was equivalent to plants grown with inorganic phosphate at 2208 mg kg(-1), and arsenic was increased from 1777 to 2630 mg kg(-1). After 2 h of mixing with three soils, P. vittata phytase retained more activity, decreasing from ∼ 26 to ∼ 25 nmol Pi mg(-1) protein min(-1), whereas those from Pteris ensiformis and wheat decreased from ∼ 18 to ∼ 1 nmol Pi mg(-1) protein min(-1). These results suggest P. vittata has a uniquely stable phytase enabling its P acquisition in P-limiting soil environments. Furthermore, the P. vittata phytase has potential use as a soil amendment, a transgenic tool, or as a feed additive supplement, reducing the need for nonrenewable, polluting P fertilizers.

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We evaluated the ability of As-hyperaccumulator Pteris vittata (PV) to remove As from As-contaminated soils over five harvests in 2.5 years in raised beds (162 kg soil/bed). We tested the hypothesis that a P-limiting environment would enhance PV growth and As uptake owing its unique ability to uptake P under As-rich environment. In Dec. 2009, PV was transplanted to three As-contaminated soils (pH of 5.5-7.2) containing 25-129 mg kg(-1) As, which was amended with sparingly-soluble phosphate rock (PR-soil) or soluble P fertilizer (P-soil). During the 2.5-year, PV obtained sufficient P (1882 vs 2225 mg kg(-1)) from PR-soils, with increased root biomass (33%) and root exudation (53%) compared to P-soils. In addition, its frond biomass increased by 20% consecutively with each harvest (six month interval) from 18 to 36 g plant(-1). Its frond biomass in PR-soils (52.2 g plant(-1) year(-1) or ∼12 mt ha(-1) year(-1)) averaged 39% more than that in P-soils. To our knowledge, this represented the largest PV frond biomass reported, demonstrating the unique ability of PV in using insoluble P from PR in alkaline soils. In addition to biomass increase, PV from PR-soils had ∼1.5 times more As in fronds (2540, 780, and 920 mg kg(-1)) than those from P-soils (1740, 570, and 400 mg kg(-1)), with soils containing 129, 25, and 30 mg kg(-1) As, respectively. The low available P in PR-soils induced substantial plant growth and As uptake by PV. This translated into significantly more As removal from soil, averaging 48% reduction in PR-soils and 36% in P-soils in 2.5 years. With multiple harvests and PR amendments, our results showed As removal by PV from contaminated soils was ∼7 times faster than published studies.

The aim of this work was to investigate the ability of Acidovorax avenae ssp. citrulli, the causal agent of bacterial fruit blotch of cucurbits (BFB), to colonize female watermelon blossoms, and to explore the relationship between blossom inoculum dosage and seed infestation. Under greenhouse conditions A. avenae ssp. citrulli colonized stigmas and styles of female watermelon blossoms reaching populations of %10 7 to 10 8 colony-forming units (CFU) per blossom for 96 h after inoculation. Acidovorax avenae ssp. citrulli growth on stigmas was slower than that of Pseudomonas syringae Cit7, a non-pathogenic, foliar epiphyte of tomato. While pollination reduced growth of A. avenae ssp. citrulli, but P. syringae Cit7 was unaffected. Both bacteria colonized style tissues but bacterial growth in the style was significantly less than the stigma. Blossom inoculation with %1 · 10 3 A. avenae ssp. citrulli CFU/blossom led to 36-55% infested seedlots within symptomless fruits. On average 14% of the seedlings produced from these seedlots displayed BFB symptoms. There was a strong positive correlation between A. avenae ssp. citrulli inoculum concentration applied to blossoms and the percentage of infested seedlots, as determined by the seedling grow-out assay (R 2 ¼ 0.94). However, this relationship was weaker when seedlot infestation was determined by a polymerase chain reaction-based assay (R 2 ¼ 0.34). There was also a strong positive linear relationship between A. avenae ssp. citrulli blossom inoculum dose and the mean percentage of BFB-infected seedlings (R 2 ¼ 0.99) produced in seedling grow-out assays. These data support the hypothesis that blossom colonization might be involved in seed infestation under field conditions.

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