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Arsenic is a toxic metalloid and recognized carcinogen. Arsenate and arsenite are the most common arsenic species available for uptake by plants. As an inorganic phosphate (Pi) analog, arsenate is acquired by plant roots through endogenous Pi transport systems. Inside the cell, arsenate is reduced to the thiol-reactive form arsenite. Glutathione (GSH)-conjugates of arsenite may be extruded from the cell or sequestered in vacuoles by members of the ATP-binding cassette (ABC) family of transporters. In the present study we sought to enhance both plant arsenic uptake through Pi transporter overexpression, and plant arsenic tolerance through ABC transporter overexpression. We demonstrate that Arabidopsis thaliana plants overexpressing the high-affinity Pi transporter family members, AtPht1;1 or AtPht1;7, are hypersensitive to arsenate due to increased arsenate uptake. These plants do not exhibit increased sensitivity to arsenite. Co-overexpression of the yeast ABC transporter YCF1 in combination with AtPht1;1 or AtPht1;7 suppresses the arsenate-sensitive phenotype while further enhancing arsenic uptake. Taken together, our results support an arsenic transport mechanism in which arsenate uptake is increased through Pi transporter overexpression, and arsenic tolerance is enhanced through YCF1-mediated vacuolar sequestration. This work substantiates the viability of coupling enhanced uptake and vacuolar sequestration as a means for developing a prototypical engineered arsenic hyperaccumulator.
Long-term human exposure to arsenic has been linked to an increased incidence of several cancers and non-cancer skin pathologies (Akter et al., 2005; Duker et al., 2005; Smith et al., 1992). Unfortunately, environmental levels of arsenic exceeding safe standards set by the WHO and EPA are found at many locations worldwide [e.g. India (Patel et al., 2005), Bangladesh (Smith et al., 2000), China (Xia and Liu, 2004), Vietnam (Berg et al., 2001), Australia (Smith et al., 2003), and the U.S. (Durant et al., 2004; Erickson and Barnes, 2005; Welch et al., 2000)]. Concerned over the health issues associated with arsenic pollution, we seek to develop strategies for extracting arsenic from contaminated water and soil (Meagher et al., 2007).
Arsenic is present in the majority of aerobic soils as the toxic oxyanion arsenate (AsO4−3). Due to its chemical similarity to inorganic phosphate (Pi; PO4−3), arsenate gains access to plant cells by hijacking endogenous Pi transport systems (Abedin et al., 2002; Meharg and Macnair, 1990; Wang et al., 2002). Due to the essential roles Pi plays in growth and development, plants have evolved a variety of responses to facilitate uptake under Pi-limiting conditions (Raghothama, 1999; Yang and Finnegan, 2010). One such response is the induction of high-affinity Pi transporter expression (Muchhal et al., 1996; Shin et al., 2004). The mobilization of phosphorus from mature shoot tissues to actively growing tissues is another Pi starvation response (Jeschke et al., 1997; Mudge et al., 2002; Nagarajan et al., 2011), which may be achieved in part through regulation of Pi transporter expression. The Arabidopsis genome encodes nine high-affinity Pi transporters (Pht1;1 – Pht1;9, hereafter called PHT1 – PHT9), eight of which are induced in roots under Pi-deficient conditions (PHT1-5 and PHT7-9; Mudge et al., 2002). While the relative contribution of the nine Arabidopsis PHT family members to arsenic uptake is not yet known, PHT1 and PHT4 have both been implicated in arsenate transport. pht1 null mutants are moderately arsenate tolerant, while pht1 pht4 double mutants are significantly arsenate tolerant, indicating that arsenic uptake is compromised by mutations in these Pi transporters (Shin et al., 2004). Plants overexpressing PHT1, on the other hand, have been shown to be arsenate-sensitive (Catarecha et al., 2007). In the present study, we sought to increase plant arsenic uptake through overexpression of the high-affinity Arabidopsis Pi transporters PHT1 (PHT1ox) and PHT7 (PHT7ox).
Several members of the ATP-binding cassette (ABC) transporter family have been implicated in the transport of arsenic across membranes. For example, HsABCC1/HsMRP1 over-expression has been linked to arsenic resistance in a tumor-derived cell line (Vernhet et al., 1999). Furthermore, HsABCC1 homologs contribute to arsenic detoxification in the nematode Caenorhabditis elegans (Broeks et al., 1996; Schwartz et al., 2010), the protozoan Leishmania tarentolae (Papadopoulou et al., 1994), and the yeast Saccharomyces cerevisiae (Song et al., 2003; Guo et al., 2012). Whereas HsABCC1 is found at the plasma membrane, the ABC transporter Yeast Cadmium Factor 1 (YCF1) has been localized to the vacuolar membrane in both yeast (Wemmie and Moye-Rowley, 1997) and transgenic Arabidopsis plants (Song et al., 2003). Several YCF1 homologs in plants have been found at the tonoplast as well (Jaquinod et al., 2007; Klein et al., 2006; Liu et al., 2001). More recently, two transporters in Arabidopsis, AtABCC1 and AtABCC2, were shown to contribute to arsenic tolerance via vacuolar sequestration of As(III)-phytochelatin conjugates (Song et al., 2010). While plasma membrane ABC transporters are involved in substrate extrusion, vacuolar ABC transporters are involved in substrate sequestration. Although both cellular extrusion and vacuolar sequestration of arsenic are viable mechanisms for arsenic detoxification, only vacuolar sequestration would result in the combination of increased arsenic resistance and accumulation. In the present study we sought to increase plant arsenic resistance through overexpression of yeast YCF1 (YCF1ox).
Coupling two intuitively mutually exclusive activities - increased arsenic uptake and increased arsenic tolerance - is essential to engineering a plant appropriate for arsenic phytoremediation. Toward this end, we created transgenic Arabidopsis plants overexpressing Arabidopsis Pi transporters (PHT1ox or PHT7ox) either alone or in combination with YCF1ox. Analysis of the transgenic plants revealed that overexpression of PHT1, PHT7, or YCF1 enhanced plant arsenic accumulation. Furthermore, coupling PHT- and YCF1-overexpression conferred both enhanced arsenic tolerance and accumulation on transgenic plants. Our results support the viability of coupling enhanced uptake with enhanced vacuolar sequestration as a means for developing a prototypical engineered arsenic hyperaccumulator.
For all experiments, wild-type Arabidopsis thaliana (ecotype Columbia) and transgenic seeds were surface-sterilized and grown under a long-day photoperiod (16 h light / 8 h dark) at 22°C with an average light intensity of 60 μmol m−2 s−1. Seedlings were grown on plates containing half-strength Murashige and Skoog (MS) salts (Murashige and Skoog, 1962) with 1% (wt/vol) sucrose (MS plates) for the duration indicated. For assaying arsenate exposure phenotypes and quantifying transgene abundance, plants were grown on MS plates supplemented with 1.2% (vertically-oriented) or 1.0% (horizontally-oriented) agar (Caisson). Otherwise, MS media was solidified with agar (Type E, Sigma) concentrations of 0.5% for horizontally oriented plates and 0.9% for vertically oriented plates. To generate Pi-starved tissue for PHT1 and PHT7 cDNA amplification, seedlings were grown in liquid MS media on a rotary shaker for 10 d and subsequently transferred to MS media lacking Pi for an additional 2 d. For seedling treatments, sodium arsenite, sodium arsenate, or buthionine sulfoximine (Sigma) was added to plant media after autoclaving at the indicated concentration from an aqueous, sterile stock solution.
RNA was isolated using the Spectrum Plant Total RNA Kit (Sigma), except for transgene quantification experiments, which utilized the Qiagen RNeasy plant mini kit (Qiagen). One microgram of RNA was DNAse treated using RQ1 RNAse-free DNAse (Promega), and complementary DNA synthesis was performed with an oligo(dT)20 primer using the Superscript III First-Strand Synthesis System for RT-PCR (Invitrogen). Twenty μL reaction volumes containing 2 μM each of sense and antisense primers, 4 μL of 20-fold diluted cDNA, and 10 μL SYBR Green PCR Master Mix (Applied Biosystems) were used for quantitative RT-PCR (qRT-PCR) experiments using an Applied Biosystems 7500 Real-Time PCR instrument. The ACTIN2 transcript was used as the endogenous control, and relative expression levels for each Arabidopsis Pi transporter were calculated based on four to six replicates using the 2−ΔΔCt method of relative quantification (Livak and Schmittgen, 2001). These data were normalized to transcript abundance in untreated control tissues. The transcript abundance of YCF1, PHT1 or PHT7 in overexpression lines relative to wild-type plants was expressed as 2−ΔCt rather than 2−ΔΔCt since the YCF1 transcript is not detected in wild-type Arabidopsis.
The 4548 nucleotide YCF1 coding sequence was amplified in two pieces from genomic DNA isolated from the BY4742 S. cerevisiae parental strain produced by the Saccharomyces Genome Deletion Project (http://www-sequence.stanford.edu/group/yeast_deletion_project/deletions3.html) and assembled using overlap extension PCR (Ho et al., 1989). The 5′ half of YCF1 (2.6 Kb) was modified during PCR to eliminate an internal NcoI site, using the primers YCF1-XhNcIS, YCF1-NcMutN, YCF1-NcMutS, and YCF1-PstIN (all primer sequences are shown in Table S1). This 2.6 Kb fragment was cloned into pBluescript KS via the XhoI and PstI restriction sites (pBS::YCF1-2.6). The 3′ half of YCF1 (2.0 Kb) was amplified using the primers YCF1-PstIS and YCF1-ScBmN, and cloned into pBS::YCF1-2.6 using the PstI and BamHI restriction sites (pBS::YCF1). The NcoI and BamHI restriction sites flanking YCF1 were used to subclone the YCF1 coding sequence into a constitutive vegetative ACTIN2 promoter/terminator cassette (A2pt) (described in Kandasamy et al., 2002), within the binary vector pCambia-1300 (pCambia::A2pt::YCF1).
The PHT1 and PHT7 cDNAs were amplified from total RNA extracted from 12-day-old wild-type Arabidopsis seedlings that had been starved for Pi for two days. The PHT1 sequence was modified using overlap extension PCR (Ho et al., 1989) to eliminate an internal NcoI site, with the primers PHT1_S1, PHT1_A894, PHT1_S863, and PHT1_A1575noHA. A single set of flanking primers was used to amplify the constructed sequence (PHT1_flank_S and PHT1_flank_A) prior to cloning into an ACTIN2 promoter/terminator cassette (Kandasamy et al., 2002) via NcoI and HindIII restriction sites within the binary vector pCambia-1300 (pCambia::A2pt::PHT1). The PHT7 sequence was amplified in 3 pieces and modified using overlap extension PCR (Ho et al., 1989) to eliminate internal BspHI and KpnI restriction sites. A second KpnI site was eliminated via point mutation in the PHT7_S1 primer. In addition, a serine codon was inserted following the methionine start to maintain in-frame cloning via a NcoI restriction site. The primers used for amplification were: PHT7_S1, PHT7_A876, PHT7_S845, PHT7_A1073, PHT7_S1045, and PHT7_A1608noHA. A single set of flanking primers was used to amplify the constructed sequence (PHT7_flank_S and PHT7_flank_A) prior to cloning into the ACTIN2 promoter/terminator cassette via NcoI/BspHI and SalI restriction sites within the binary vector pCambia-1300 (pCambia::A2pt::PHT7).
Wild-type Arabidopsis plants were transformed independently with each membrane transporter overexpression construct using Agrobacterium-mediated transformation (Clough and Bent, 1998). PCR analysis of genomic DNA from hygromycin-resistant plants using one vector-specific and one gene-specific primer was used to verify the presence of the correct transgene within each plant line. The segregation of hygromycin resistance was used to identify T3 plant lines homozygous for each construct. YCF1 and PHT1 or PHT7 co-overexpression plants were generated through cross-fertilization between appropriate transgenic plants.
Plant samples were swirled for 2 min in 0.01 M HCl, followed by two rinses in deionized water to remove residual arsenic-containing media from tissue surfaces (Aldrich et al., 2003). The samples were prepared for elemental analysis based on methods described in Li et al., 2004. Samples were dried for 3d at 60° C. Prior to arsenic analysis, dried plant tissue was digested overnight with 7 parts nitric acid : 1 part perchloric acid, diluted with water, and passed through a 0.45 micron syringe filter unit. Arsenic levels in these samples were determined using ICP-OES (Chemical Analysis Laboratory, Center for Applied Isotope Studies, University of Georgia).
Seedlings were germinated on MS plates, oriented vertically. 5-day old seedlings were transferred to a new MS plate supplemented with 250 μM BSO or 100 μM sodium arsenate, or both chemicals. At the time of transfer, root tips were marked with a dot on the bottom of the Petri plate. Following three additional days of growth, Image J was used to measure the length of root growth in pixels from the dot to the new location of the root tip (Abramoff et al., 2004).
Sulfhydryl groups were quantified in seedlings exposed to BSO, arsenate, or both (as described above), using Ellman’s Reagent [DTNB, (Ellman, 1959), Pierce Protein Research Products, Thermo Fisher Scientific] based on a method modified from Lee et al (2003). Approximately 100 mg of plant tissue was ground in liquid nitrogen and resuspended in 300 μL 1 M NaOH and 1 mg/L NaBH4. After a 5 min spin at 13,000 x g at 4° C, the supernatant was moved to a new tube, and 50 μL of concentrated HCl was added. Samples were vortexed briefly and spun at 13,000 x g for 5 min at room temperature. Eighty μL of supernatant was transferred to a new tube containing 1 mL of reaction buffer (0.1 M sodium Pi pH 8.0, containing 5 mM EDTA) and 20 μL of 4 mg/mL Ellman’s reagent. Samples were incubated for 15 min at 30° C, at which time the absorbance at A412 nm was recorded relative to blanked control with reaction buffer.
Where indicated, statistical significance was determined using Student’s t-Test (p < 0.05), and standard deviations or standard errors are shown in the bar graphs.
We assayed the transcript abundance of the Arabidopsis high-affinity Pi transporter (PHT) family in shoot and root tissues of arsenic-exposed seedlings. Observing increased PHT transcript abundance in response to arsenate may deem one or more PHT proteins worthy of targeting for enhancing arsenate acquisition. However, no PHT transcripts were induced in shoots or roots of plants exposed to 150 μM sodium arsenate for 21 days, but rather, PHT8 transcript abundance decreased 5.6-fold in roots (Fig. 1; PHT3 and PHT6 transcripts were consistently below the limit of detection in our assays). Since arsenate exposure did not implicate any PHTs in arsenate acquisition from the substrate by roots, we selected one vegetative (PHT1) and one reproductive (PHT7) Pi transporter for constitutive overexpression in wild-type Arabidopsis plants, based on their contrasting root and floral RNA expression levels, respectively (Mudge et al., 2002; Fig. 2).
We cloned the coding sequences of each of PHT1, PHT7, and YCF1 into binary vectors for plant expression, under the control of the constitutive, vegetative ACTIN2 promoter and terminator sequences (A2pt; Kandasamy et al., 2002). Agrobacterium-mediated transformation was used to independently introduce the A2pt::PHT1 (PHT1ox), A2pt::PHT7 (PHT7ox), and A2pt::YCF1 (YCF1ox) constructs into wild-type Arabidopsis. Plant lines homozygous for a single insertion of each transgene were identified by hygromycin resistance of the T3 generation, and used to generate PHT1oxYCF1ox and PHT7oxYCF1ox co-overexpressing plant lines through crossing. Overexpression of the YCF1, PHT1, and PHT7 transgenes in the lines selected for further study were verified using quantitative Reverse Transcription-Polymerase Chain Reaction (qRT-PCR; Fig. 3). Transcript levels from each transgene were lower in the co-overexpression lines as compared to the parental, single transformants, although expression of the endogenous ACT2 gene was unaffected, as determined via qRT-PCR analysis (data not shown). This could be the result of partial silencing of the ACT2 promoters driving transgene expression, but not of the endogenous ACT2 promoter, through small RNA-dependent promoter methylation (Eamens et al., 2008). Indeed, endogenous promoters appear less sensitive to this co-suppression silencing mechanism than transgene promoters (Okano et al., 2008).
Initial screening of segregating YCF1ox lines in the presence of arsenate (200 μM) demonstrated that YCF1-overexpression conferred arsenate tolerance on 30-day-old Arabidopsis seedlings (Fig. 4A), presumably due to vacuolar sequestration of arsenic via the transport activity of YCF1. In contrast, assaying the growth of several independent PHT1ox and PHT7ox lines in the presence of arsenate (150 μM) demonstrated that PHT-overexpression conferred arsenate sensitivity on 30-day-old Arabidopsis seedlings (Fig. 4B), presumably due to elevated arsenate uptake. YCF1ox and PHTox co-overexpression lines were generated based on the hypothesis that the in planta activities of these transporters would complement each another. Indeed, overexpression of the YCF1 transgene in a PHTox background rescued the arsenate-sensitivity of the PHTox lines (Fig. 4B). Based on visual screening for the best growth on arsenate, lines A2pt::PHT1-16 x A2pt::YCF1-16 (PHT1oxYCF1ox) and A2pt::PHT7-8 x A2pt::YCF1-16 (PHT7oxYCF1ox) were selected for further study (Fig. 4A,B). Whole-seedling fresh weights of 30-day-old plants grown on 150 μM arsenate were measured to quantify the arsenate tolerance/sensitivity of the various transgenic lines. Both PHToxYCF1ox co-expression lines accumulated at least 2.5-fold more biomass than the wild type, and approximately 4-fold more biomass than each corresponding single PHTox-expressor (Fig. 4C). Separating root and shoot fresh weights indicated that root growth in the co-expressors is enhanced to a greater extent than shoot growth relative to wild type (Supplementary material, Fig. S1). This may be linked to a change in root morphology in plants containing a PHT1ox or PHT7ox transgene (Supplementary material, Fig. S2), which could be the result of altered Pi uptake/homeostasis and/or increased arsenate accumulation (see below). Notably, relative to wild-type plants, PHT1ox and PHT7ox plants were not hypersensitive to arsenite (AsO3−3), the electrochemically reduced form of arsenate (Supplementary material, Fig. S3).
The arsenic content of seedlings grown in the presence of 150 μM sodium arsenate for 21 days was measured using Inductively Coupled Plasma - Optical Emission Spectrometry (ICP-OES; Fig. 5). Both PHT1ox and PHT7ox plants accumulated significantly higher arsenic levels than wild-type plants (p < 0.05), consistent with increased arsenate acquisition in these lines. Similarly, YCF1ox plants contained significantly higher As levels than wild type (p < 0.05), consistent with previously reported vacuolar metal-sequestering activities of YCF1 in yeast cells (Ghosh et al., 1999) and transgenic Arabidopsis (Guo et al., 2012). Whereas YCF1ox, PHT1ox, and PHT7ox lines contained 125% to 135% higher arsenic levels relative to wild type, PHToxYCF1ox co-expressors accumulated significantly higher arsenic levels (~150%; p < 0.05).
Arsenate exposure induces glutathione (GSH) synthesis in plants, and in so doing, increases in planta sulfhydryl levels (Li et al., 2004; Schat et al., 2002; Srivastava et al., 2009). The synthetic amino acid buthionine sulfoximine (BSO), on the other hand, inhibits GSH synthesis (Griffith and Meister, 1979), depleting in planta sulfhydryl levels. We quantified the effect of GSH depletion by BSO treatment on root arsenate-sensitivity of PHTox, YCF1ox, and PHToxYCF1ox plants. Five-day old seedlings were exposed to 250 μM BSO, 100 μM arsenate, or both chemicals for 3 days, and the change in primary root elongation was measured (Fig. 6A). The root growth of transgenic plants was not significantly altered by BSO, relative to wild-type plants (p < 0.05). In contrast, root growth of all transgenic lines was more sensitive to arsenate compared to wild type (p < 0.05), which may reflect the increased arsenate accumulation in these lines (Fig. 5). This was surprising based on our data from 30-day-old plants grown on 150 μM arsenate, in which the PHToxYCF1ox co-expressors exhibited increased root biomass relative to wild type (Supplementary material, Fig. S1). This apparent discrepancy likely reflects a difference in root morphology (Supplementary material, Fig. S2; see Discussion). Root growth of PHTox seedlings was more sensitive to arsenate or the combination of arsenate and BSO than YCF1ox seedlings (p < 0.05; Fig. 6A). Also, depletion of GSH magnified root arsenate sensitivity in all PHTox and PHToxYCF1ox lines, as compared to YCF1ox, with the PHToxYCF1ox co-expressors being less sensitive than lines overexpressing only PHT1 or PHT7 (p < 0.05; Fig. 6A). Together these results highlight the importance of GSH in compensating for the increased cytotoxic effects of elevated arsenic uptake in the PHTox and PHToxYCF1ox lines, and that although GSH is also required for the arsenic-transporting activity of YCF1, the level of GSH depletion achieved by 250 μM BSO exposure was not enough to eliminate the beneficial effect of YCF1 overexpression. However, increasing the concentrations of arsenate and BSO to 150 μM and 500 μM, respectively, did eliminate the beneficial role of YCF1 (Supplementary material, Fig. S4).
To further characterize the role of GSH and other thiols in the arsenate-responses of the transgenics, we quantified free sulfhydryl levels in all genotypes exposed to 250 μM BSO, 100 μM arsenate, or both chemicals, using Ellman’s reagent (Fig. 6B). As expected, all genotypes contained significantly elevated free sulfhydryl levels in the presence of 100 μM arsenate relative to exposure to 250 μM BSO (p < 0.05). Intermediate free sulfhydryl levels were observed in all genotypes when plants were treated with both 100 μM arsenate and 250 μM BSO. This result is consistent with the contrasting effects of arsenate [stimulatory (Li et al., 2006)] and BSO [inhibitory (Griffith and Meister, 1979)] on cellular thiol peptide levels. Notably, thiol peptide levels of YCF1ox plants were comparable to those of wild-type plants in the presence of arsenate. In contrast, the PHToxYCF1ox plants contained higher free sulfhydryl levels in the presence of arsenate than plants overexpressing YCF1 alone, but did not have elevated thiol levels relative to PHTox plants in the presence of BSO and arsenate (p < 0.05; Fig. 6B). Thus, the enhanced root growth seen in the PHToxYCF1ox lines grown under these conditions, relative to PHTox lines, (Fig. 6A) is not linked to a direct de novo increase in free sulfhydryl levels, but is likely due to enhanced vacuolar sequestration activity of YCF1.
The form of phosphorus available to plant roots for uptake and assimilation is inorganic phosphate (Pi). Unfortunately, one of the most common environmental forms of the toxic metalloid arsenic is the Pi analog, arsenate. Due to the chemical similarity between Pi and arsenate, arsenate is absorbed by plant roots through the Pi transport system (Abedin et al., 2002; Meharg and Macnair, 1990; Wang et al., 2002). Hence, suppression of high-affinity Pi transport systems seems to be a common mechanism for acquired arsenic tolerance (Meharg and Macnair, 1992). This is consistent with our observation of decreased PHT8 transcripts in roots of arsenate-treated plants (Fig. 1). Similarly, Catarecha et al (2007) reported repression of the Pi transporter PHT1 in Pi-starved plants (3d) exposed to arsenate (8h).
Because arsenate has been shown to enter plants via the Pi transport system, and pht1 pht4 double mutants in Arabidopsis exhibit increased tolerance to arsenate (Shin et al., 2004), we reasoned that over-expression of high-affinity Pi transporters in Arabidopsis would lead to plants with increased arsenate uptake. Based on the tissue localization of members of the Arabidopsis PHT family (Mudge et al., 2002), we chose one vegetatively expressed (PHT1) and one reproductively expressed (PHT7) Pi transporter for our studies. Our qRT-PCR studies on seedlings grown under Pi-replete conditions confirmed the vegetative expression previously seen for PHT1 and floral expression for PHT7 (Fig. 2). We chose to include both a vegetative and a reproductive PHT in our study in case either of these two classes of Pi transporters has evolved an ability to discriminate between arsenate and Pi.
Catarecha et al (2007) demonstrated that overexpression of PHT1 (35S::PHT1) conferred increased arsenate sensitivity on plants. Herein, we showed that overexpression of the Pi transporters PHT1 (A2pt::PHT1; PHT1ox) or PHT7 (A2pt::PHT7; PHT7ox) conferred arsenate sensitivity (Fig. 4), as well as enhanced arsenic accumulation (Fig. 5). We also demonstrated that the PHTox plants are not sensitive to the closely related, but chemically reduced oxyanion, arsenite (Supplementary material, Fig. S3). This result is consistent with previously published reports that arsenite is not taken up through the Pi transport system in plants (Abedin et al., 2002; Bienert et al., 2008; Isayenkov and Maathuis, 2008). Under our conditions, PHT7ox plants appeared marginally more sensitive to arsenate than PHT1ox plants (Supplementary material, Fig. S1, Fig. 4, and Fig. 6A), but accumulated about the same quantity of arsenic (Fig. 5). Since PHT7 transcript abundance was greater in PHT7ox plants relative to PHT1 in corresponding PHT1ox plants, the expression level of a given PHT may impact root biomass in a dosage-dependent manner by modulating root morphology, which does not directly correlate with arsenic accumulation. Additional evidence for this is seen with the PHToxYCF1ox co-expressors (see below).
Yeast YCF1 was originally identified for its role in vacuolar cadmium sequestration in yeast (Li et al., 1996; Szczypka et al., 1994), and subsequently shown to transport GSH conjugates of not only cadmium, but also mercury (Gueldry et al., 2003) and arsenic (Ghosh et al., 1999). Overexpression of YCF1 (35S:YCF1) was shown to confer both enhanced resistance to, and accumulation of, lead and cadmium on Arabidopsis plants (Song et al., 2003). Recently, Guo et al. (2012) confirmed increased cadmium accumulation and tolerance of transgenic Arabidopsis overexpressing YCF1 (35S:YCF1), and also showed increased arsenic accumulation and tolerance in these plants. Similarly we demonstrated that overexpression of YCF1 (A2pt::YCF1) conferred enhanced arsenate resistance (Fig. 4) and accumulation (Fig. 5) to Arabidopsis plants.
By coupling YCF1ox with overexpression of PHT1 or PHT7, we showed further enhancement of arsenate tolerance and accumulation (Fig. 4 and Fig. 5). Although both shoot and root fresh weights of 30-day-old PHToxYCF1ox co-expressors grown on 150 μM arsenate were greater than wild type, as well as YCF1ox and PHTox single expressors (Supplementary material, Fig. S1 and Fig. 4), short-term primary root growth assays of young seedlings showed decreases in the PHToxYCF1ox lines compared to wild type (Fig. 6A). This likely reflects a difference in root morphology that correlates with PHTox. Specifically, compared to wild type, all transgenic lines containing a PHT-overexpression transgene have relatively shorter primary roots, but greater proliferation of lateral roots, when grown in the presence of arsenate (Supplementary material, Fig. S2). This is consistent with the transgenics overexpressing PHT1 or PHT7 having relatively slower primary root growth in the seedling stage (Fig. 6A), but having greater total root mass at maturity, relative to wild type (Fig. 4C and Supplementary material, Fig. S1). It is possible that increased arsenate acquisition due to PHT-overexpression alters root system architecture (RSA), and that the addition of YCF1ox to PHT-overexpressors can compensate for the increased arsenic accumulation, ultimately leading to greater root proliferation, but it cannot reestablish the normal RSA program. This is further supported by comparing the arsenic accumulation and root biomass of all the PHT transgenic lines. In comparing the single PHT-overexpressors, PHT7 expression is 1.75-fold higher than PHT1 expression (Fig. 3), whereas PHT1ox plants have 1.3-fold higher root biomass than PHT7ox plants (Supplementary material, Fig. S1). Similarly, in the PHToxYCF1ox co-overexpression lines, PHT7 expression is 2.6-fold higher than PHT1 (Fig. 3), and the root biomass of PHT1oxYCF1ox plants is 1.3-fold higher than that of PHT7oxYCF1ox plants (Supplementary material, Fig. S1). In contrast, the accumulation of arsenic is not statistically different between PHT1ox and PHT7ox or between PHT1oxYCF1ox and PHT7oxYCF1ox. This suggests that root biomass is more tightly linked to the level of PHT expression than arsenic accumulation. A threshold level of PHT expression appears sufficient for enhanced arsenic accumulation when co-expressed with YCF1, but root biomass may be more affected by specific PHT expression levels in a way not directly related to arsenate uptake capacity, but perhaps through a more fundamental impact on RSA.
Depletion of GSH by BSO magnified root arsenate sensitivity in all plants overexpressing PHT1 or PHT7 (Fig. 6A). This highlights the importance of GSH in plant arsenic tolerance. In addition to bringing in more arsenate than wild type, we show that PHTox plants also require a higher intracellular GSH concentration than wild type to support plant growth in the presence of elevated arsenic levels. GSH plays an important role in arsenic detoxification by binding the reduced oxyanion arsenite, to create the arsenite:trisglutathione substrates for ABC transporters such as YCF1 (Ghosh et al., 1999). Hence, the arsenic-transporting activity of YCF1 depends on GSH. The PHToxYCF1ox co-expressors were less sensitive to the combination of arsenate and BSO than PHTox alone (Fig. 6A). Also, the PHToxYCF1ox co-expressors contained lower or comparable sulfhydrl levels relative to the PHTox lines under these conditions. Together these results suggest that YCF1 activity is less dependent on de novo GSH synthesis than the ability to tolerate increased arsenate acquisition resulting from PHT-overexpression. However, because YCF1-mediated arsenic transport activity requires GSH, further depletion of GSH by BSO should phenocopy the PHTox root arsenate sensitivity in the PHToxYCF1ox lines. Indeed, we demonstrated that in the presence of higher arsenate and BSO concentrations (150 μM and 500 μM, respectively) the arsenate sensitivity of PHTox lines was phenocopied in PHToxYCF1ox lines (Supplementary material, Fig. S4).
In conclusion, we demonstrate that Arabidopsis plants overexpressing PHT1 or PHT7 are hypersensitive to arsenate, due to increased arsenic uptake. These plants do not exhibit increased sensitivity to externally supplied arsenite. Co-overexpression of yeast YCF1 with the PHT1 or PHT7 Pi transporters both enhances PHTox-mediated arsenic accumulation, and alleviates PHTox-induced arsenate sensitivity. Taken together, our results support an arsenic transport mechanism in which arsenate uptake is enhanced through Pi transporter overexpression, while arsenic resistance is enhanced through YCF1-mediated vacuolar sequestration.
Fig. S1. Arsenate phenotypes of transgenic Arabidopsis plants overexpressing PHT and/or YCF1. Wild-type (WT) and homozygous transgenic lines were grown on 150 μM sodium arsenate for 30 days. Average fresh weights of roots, shoots, or whole seedlings are shown normalized to the weights in the corresponding tissue from WT. Error bars indicate standard deviation, n > 60.
Fig. S2. Seedling morphology of transgenic Arabidopsis plants overexpressing PHT and/or YCF1 trangenes. Plants were grown on plates in the presence (right) or absence (left) of 150 μM sodium arsenate (AsV) for 21 days.
Fig. S3. PHT-overexpression does not confer sensitivity to arsenite. The average seedling fresh weights of wild-type (WT) and PHT1- or PHT7-overexpression plants grown on 25 μM sodium arsenite for 21 days were quantified. Error bars indicate standard deviation, n > 25.
Fig. S4. Glutathione depletion phenocopies the arsenate-sensitivity of PHT1ox and PHT7ox plants in PHToxYCF1ox co-expressors. Root elongation was quantified for 7-day-old wild-type (WT) and transgenic plants grown for 5 days in the presence of 150 μM sodium arsenate (left) or 150 μm sodium arsenate and 500 μM BSO (right). Black dots mark the location of seedling root tips at the time of transfer from control media to media containing arsenate or arsenate and BSO.
Table S1. Primers used in the current study.
We thank Yolanda Lay for assistance with plant care, and anonymous reviewers for helpful comments. This research was supported by a grant to R.B.M. from the U.S. Department of Energy’s Office of Biological and Environmental Research (DEG0796ER20257), by a NIH National Research Service Award to M.S.L. (1F32ES015414), and by funds to A.P.S. from Louisiana State University.
Supplementary material associated with this article can be found in the online version.
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