7 research outputs found
Impact of Ag Nanoparticle Exposure on <i>p,p′</i>-DDE Bioaccumulation by Cucurbita pepo (Zucchini) and Glycine max (Soybean)
The effect of nanoparticle (NP), bulk, or ionic Ag exposure
on
dichlorodiphenyldichloroethylene (<i>p,p′</i>-DDE;
DDT metabolite) accumulation by Glycine max L. (soybean) and Cucurbita pepo L.
(zucchini) was investigated. The plants were grown in 125-mL jars
of vermiculite amended with 500 or 2000 mg/L of bulk or NP Ag; ion
controls at 5 and 20 mg/L were established. During 19 d of growth,
plants were amended with solution containing 100 ng/mL of <i>p,p′</i>-DDE. Total shoot <i>p,p′</i>-DDE levels in non-Ag exposed G. max and C. pepo were 500 and 970 ng,
respectively; total root DDE content was 13 700 and 20 300
ng, respectively. Ag decreased the <i>p,p′</i>-DDE
content of G. max tissues by up to
40%, with NP exposure resulting in less contaminant uptake than bulk
Ag. Total Ag content of exposed G. max ranged from 50.5 to 373 μg; NP-exposed plants had 1.9–2.2
times greater overall Ag than corresponding bulk particle treatments
and also significantly greater relative Ag transport to shoot tissues.
Bulk and NP Ag at 500 mg/L suppressed DDE uptake by C. pepo by 21–29%, although Ag exposure at
2000 mg/L had no impact on contaminant uptake. Similar to G. max, C. pepo whole
plant Ag content ranged from 50.5 to 182 μg, with tissue element
content generally being greater for NP exposed plants. These findings
show that the Ag may significantly alter the accumulation and translocation
of cocontaminants in agricultural systems. Notably, the cocontaminant
interactions vary both with Ag particle size (NP vs bulk) and plant
species. Future investigations will be needed to clarify the mechanisms
responsible for the cocontaminant interactions and assess the impact
on overall exposure and risk
Fullerene-Enhanced Accumulation of <i>p</i>,<i>p</i>′‑DDE in Agricultural Crop Species
The effect of C60 fullerene exposure on the
accumulation
of dichlorodiphenyldichloroethylene (p,p′-DDE; DDT metabolite) by Cucurbita pepo L.
(zucchini), Glycine max L. (soybean), and Solanum lycopersicum L. (tomato) was determined. The plants
were grown in 125 mL jars of vermiculite amended with 0 or 40 mg of
C60 fullerenes. Prior to planting, the jars were amended
with 40 mL solution containing 100 ng/mL of p,p′-DDE with 0 or 100 mg/L humic acid. During three
weeks of growth, plants were watered with the same p,p′-DDE containing solutions. Total shoot p,p′-DDE levels in nonfullerene
exposed tomato, soybean, and zucchini were 26.9, 131, and 675 ng,
respectively; total root DDE content for the three plants was 402,
5970, and 5830 ng, respectively. Fullerenes increased the shoot p,p′-DDE content of zucchini by
29%; contaminant levels in soybean shoots were decreased by 48% but
tomato shoot content was unaffected. The root and total plant p,p′-DDE content of all three species
was significantly increased by fullerene exposure; enhanced contaminant
uptake ranged from 30 to 65%. Humic acid, regardless of fullerene
presence or plant type, significantly decreased the p,p′-DDE uptake. Fullerenes were detected
in the roots of all plants but were not detected in plant shoots in
the initial study. In a follow up study with zucchini designed to
maximize biomass for extraction, over half the analyzed stems contained
fullerenes at 60.5 to 4490 ng/g. These findings show that the carbon-based
nanomaterials may significantly alter the accumulation and potentially
the toxicity of cocontaminants in agricultural systems
Terrestrial Trophic Transfer of Bulk and Nanoparticle La<sub>2</sub>O<sub>3</sub> Does Not Depend on Particle Size
The
bioaccumulation and trophic transfer of bulk and nanoparticle
(NP) La<sub>2</sub>O<sub>3</sub> from soil through a terrestrial food
chain was determined. To investigate the impact of growth conditions,
lettuce (Lactuca sativa) was grown
in 350 or 1200 g of bulk/NP amended soil. Leaf tissues were fed to
crickets (Acheta domesticus) or darkling
beetles (Tenebrionoidea); select crickets
were fed to mantises. In the small pot (350 g), La<sub>2</sub>O<sub>3</sub> exposure reduced plant biomass by 23–30% and La tissue
content did not differ with particle size. In the large pot (1200
g), biomass was unaffected by exposure and La content in the tissues
were significantly greater with bulk particle treatment. Darkling
beetles exposed to bulk and NP La<sub>2</sub>O<sub>3</sub>-contaminated
lettuce contained La at 0.18 and 0.08 mg/kg; respectively (significantly
different, <i>P</i> < 0.05). Crickets fed bulk or NP
La<sub>2</sub>O<sub>3</sub>-exposed lettuce contained 0.53 and 0.33
mg/kg, respectively (significantly different, <i>P</i> <
0.05) with 48 h of depuration. After 7 d of depuration, La content
did not differ with particle size, indicating that 48 h may be insufficient
to void the digestive system. Mantises that consumed crickets from
bulk and NP-exposed treatments contained La at 0.05–0.060 mg/kg
(statistically equivalent). These results demonstrate that although
La does trophically transfer, biomagnification does not occur and
NP levels are equivalent or less than the bulk metal
Fullerene-Enhanced Accumulation of <i>p</i>,<i>p</i>′‑DDE in Agricultural Crop Species
The effect of C<sub>60</sub> fullerene exposure on the
accumulation
of dichlorodiphenyldichloroethylene (<i>p</i>,<i>p</i>′-DDE; DDT metabolite) by <i>Cucurbita pepo</i> L.
(zucchini), <i>Glycine max</i> L. (soybean), and <i>Solanum lycopersicum</i> L. (tomato) was determined. The plants
were grown in 125 mL jars of vermiculite amended with 0 or 40 mg of
C<sub>60</sub> fullerenes. Prior to planting, the jars were amended
with 40 mL solution containing 100 ng/mL of <i>p</i>,<i>p</i>′-DDE with 0 or 100 mg/L humic acid. During three
weeks of growth, plants were watered with the same <i>p</i>,<i>p</i>′-DDE containing solutions. Total shoot <i>p</i>,<i>p</i>′-DDE levels in nonfullerene
exposed tomato, soybean, and zucchini were 26.9, 131, and 675 ng,
respectively; total root DDE content for the three plants was 402,
5970, and 5830 ng, respectively. Fullerenes increased the shoot <i>p</i>,<i>p</i>′-DDE content of zucchini by
29%; contaminant levels in soybean shoots were decreased by 48% but
tomato shoot content was unaffected. The root and total plant <i>p</i>,<i>p</i>′-DDE content of all three species
was significantly increased by fullerene exposure; enhanced contaminant
uptake ranged from 30 to 65%. Humic acid, regardless of fullerene
presence or plant type, significantly decreased the <i>p</i>,<i>p</i>′-DDE uptake. Fullerenes were detected
in the roots of all plants but were not detected in plant shoots in
the initial study. In a follow up study with zucchini designed to
maximize biomass for extraction, over half the analyzed stems contained
fullerenes at 60.5 to 4490 ng/g. These findings show that the carbon-based
nanomaterials may significantly alter the accumulation and potentially
the toxicity of cocontaminants in agricultural systems
Particle-Size Dependent Accumulation and Trophic Transfer of Cerium Oxide through a Terrestrial Food Chain
The
accumulation and trophic transfer of nanoparticle (NP) or bulk
CeO<sub>2</sub> through a terrestrial food chain was evaluated. Zucchini
(<i>Cucurbita pepo</i> L.) was planted in soil with 0 or
1228 μg/g bulk or NP CeO<sub>2</sub>. After 28 d, zucchini tissue
Ce content was determined by ICP-MS. Leaf tissue from each treatment
was used to feed crickets (<i>Acheta domesticus</i>). After
14 d, crickets were analyzed for Ce content or were fed to wolf spiders
(family Lycosidae). NP CeO<sub>2</sub> significantly suppressed flower
mass relative to control and bulk treatments. The Ce content of zucchini
was significantly greater when exposure was in the NP form. The flowers,
leaves, stems, and roots of zucchini exposed to bulk CeO<sub>2</sub> contained 93.3, 707, 331, and 119 000 ng/g, respectively;
NP-exposed plants contained 153, 1510, 479, and 567 000 ng/g, respectively.
Crickets fed NP CeO<sub>2</sub>-exposed zucchini leaves contained
significantly more Ce (33.6 ng/g) than did control or bulk-exposed
insects (15.0–15.2 ng/g). Feces from control, bulk, and NP-exposed
crickets contained Ce at 248, 393, and 1010 ng/g, respectively. Spiders
that consumed crickets from control or bulk treatments contained nonquantifiable
Ce; NP-exposed spiders contained Ce at 5.49 ng/g. These findings show
that NP CeO<sub>2</sub> accumulates in zucchini at greater levels
than equivalent bulk materials and that this greater NP intake results
in trophic transfer and possible food chain contamination
Weathering in soil increases nanoparticle CuO bioaccumulation within a terrestrial food chain
<p>This study evaluates the bioaccumulation of unweathered (U) and weathered (W) CuO in NP, bulk and ionic form (0–400 mg/kg) by lettuce exposed for 70 d in soil co-contaminated with field incurred chlordane. To evaluate CuO trophic transfer, leaves were fed to crickets (<i>Acheta domestica</i>) for 15 d, followed by insect feeding to lizards (<i>Anolis carolinensis</i>). Upon weathering, the root Cu content of the NP treatment increased 214% (327 ± 59.1 mg/kg) over unaged treatment. Cu root content decreased in bulk and ionic treatments from 70–130 mg/kg to 13–26 mg/kg upon aging in soil. Micro X-ray fluorescence (μ-XRF) analysis of W-NP-exposed roots showed a homogenous distribution of Cu (and Ca) in the tissues. Additionally, micro X-ray absorption near-edge (μ-XANES) analysis of W-NP-exposed roots showed near complete transformation of CuO to Cu (I)-sulfur and oxide complexes in the tissues, whereas in unweathered treatment, most root Cu remained as CuO. The expression level of nine genes involved in Cu transport shows that the mechanisms of CuO NPs (and bulk) response/accumulation are different than ionic Cu. The chlordane accumulation by lettuce upon co-exposure to CuO NPs significantly increased upon weathering. Conversely, bulk and ionic exposures decreased pesticide accumulation by plant upon weathering. The Cu cricket fecal content from U-NP-exposed insects was significantly greater than the bulk or ion treatments, suggesting a higher initial NP accumulation followed by significantly greater elimination during depuration. In the lizard, Cu content in the intestine, body and head did not differ as a function of weathering. This study demonstrates that CuO NPs may undergo transformation processes in soil upon weathering that subsequently impact NPs availability in terrestrial food chains.</p
Molecular Response of Crop Plants to Engineered Nanomaterials
Functional
toxicology has enabled the identification of genes involved
in conferring tolerance and sensitivity to engineered nanomaterial
(ENM) exposure in the model plant Arabidopsis thaliana (L.) Heynh. Several genes were found to be involved in metabolic
functions, stress response, transport, protein synthesis, and DNA
repair. Consequently, analysis of physiological parameters, metal
content (through ICP-MS quantification), and gene expression (by RT-qPCR)
of A. thaliana orthologue genes were
performed across different plant species of agronomic interest to
highlight putative biomarkers of exposure and effect related to ENMs.
This approach led to the identification of molecular markers in Solanum lycopersicum L. and Cucurbita
pepo L. (tomato and zucchini) that might not only
indicate exposure to ENMs (CuO, CeO<sub>2</sub>, and La<sub>2</sub>O<sub>3</sub>) but also provide mechanistic insight into response
to these materials. Through Gene Ontology (GO) analysis, the target
genes were mapped in complex interatomic networks representing molecular
pathways, cellular components, and biological processes involved in
ENM response. The transcriptional response of 38 (out of 204) candidate
genes studied varied according to particle type, size, and plant species.
Importantly, some of the genes studied showed potential as biomarkers
of ENM exposure and effect and may be useful for risk assessment in
foods and in the environment