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<title>Plant and Soil Sciences Dissertations Collection</title>
<copyright>Copyright (c) 2013 University of Massachusetts - Amherst All rights reserved.</copyright>
<link>http://scholarworks.umass.edu/psis_diss</link>
<description>Recent documents in Plant and Soil Sciences Dissertations Collection</description>
<language>en-us</language>
<lastBuildDate>Tue, 26 Mar 2013 07:30:19 PDT</lastBuildDate>
<ttl>3600</ttl>





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<title>Biological control of the ambermarked birch leafminer (Profenusa thomsoni) in Alaska</title>
<link>http://scholarworks.umass.edu/dissertations/AAI3546056</link>
<guid isPermaLink="true">http://scholarworks.umass.edu/dissertations/AAI3546056</guid>
<pubDate>Wed, 16 Jan 2013 12:25:24 PST</pubDate>
<description>
	<![CDATA[
	<p> The ambermarked birch leafminer (AMBLM) (<i>Profenusa thomsoni</i>) is an invasive leafminer native to the Palearctic from the United Kingdom to Turkey to Japan.  It was introduced to the eastern United States in 1921 and has since spread to the mid-western U.S. states and Canadian provinces.  This leafminer was introduced to Alaska in 1996, where it has since spread over 140,000 acres, from Haines to Fairbanks.  The most severe damage is found throughout the Anchorage bowl, which extends south to Girdwood and North to Wasilla.  The damage caused by <i>P. thomsoni</i> can be severe, defoliating entire trees.   ^   In 2006, it was noted that urban areas in Alaska experienced higher densities of AMBLM leafminer than adjacent forested areas.  To examine the effects of habitat on leafminer densities, twenty permanent plots were established in Anchorage, Alaska in 2006 and were classified as urban and forest (ten each).  Temperature records for the twenty permanent sites showed that average daily temperatures and average accumulated degree-days differed significantly between urban and forest sites. In 2007 and 2008, leafminer abundance in each habitat was examined weekly at six plots (three urban and three forest) within the city of Anchorage. Asynchronous emergence, flight, and oviposition times were observed between leafminers in forests versus urban areas, with peaks of these parameters in forests being about three weeks later than in urban areas.  ^   To control the spread and effects of <i>P. thomsoni</i>, a cooperative biological control project was launched in 2003 and the parasitoid wasp <i>Lathrolestes thomsoni</i> (Hymenoptera: Tenthredinidae) was selected for release.  Parasitized leafminer larvae were collected from the provinces of Northwest Territories and Alberta, in Canada and transferred in soil tubs as pre-pupae to Alaska.  From 2004-2008, 3636 adult <i> L. thomsoni</i> adults were released in birch tree stands in Anchorage, Soldotna, and Fairbanks, Alaska.  Parasitoids have been recovered at all release sites in Alaska and have established populations at most release sites. Currently, AMBLM densities have declined by over 40% in the Anchorage area and the spread of the leafminer throughout the state appears to have slowed.  ^   Throughout the course of the biological control program two additional parasitoids were discovered attacking <i>P. thomsoni</i> in Alaska. The first, <i>Lathrolestes soperi</i>, an endoparasitoid with similar biology to the released parasitoid <i>L. thomsoni</i>, was found to attack early instar larvae within the leaf.  The second species, <i> Aptesis segnis</i>, is an ecotoparasitoid that attacks pupae and prepupae in their earthen cells in soil.  <i>Lathrolestes soperi</i> was found to contribute a significant proportion of mortality against the leafminer.  The presence of <i>A. segnis</i> in the parasitoid guild raised mortality of <i>P. thomsoni</i> to 40.3%, showing that the percent parasitism by <i>A. segnis</i> was 26%, double that provided by <i> L. soperi</i>.   This suggests that <i>A. segnis</i> is the dominant parasitoid in the guild.  It is unknown what effect that the introduced wasp <i>L. thomsoni</i> will have on the presumably native <i> L. soperi</i> and if one species will outcompete the other over time, or both will coexist.  Future work on this system is recommended in five to ten years to see if <i>L. thomsoni</i> and <i>L. soperi</i> populations remain stable or to see if one parasitoid outcompetes the other and if <i>A. segnis</i> maintains its dominant place in the system. ^</p>

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<author>Soper, Anna L</author>

<source></source>

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<title>Functional characterization of members of plasma membrane intrinsic proteins subfamily and their involvement in metalloids transport in plants</title>
<link>http://scholarworks.umass.edu/dissertations/AAI3518265</link>
<guid isPermaLink="true">http://scholarworks.umass.edu/dissertations/AAI3518265</guid>
<pubDate>Fri, 26 Oct 2012 10:58:56 PDT</pubDate>
<description>
	<![CDATA[
	<p> Aquaporins (AQPs) are channel proteins that facilitate the transport of water and various low molecular weight solutes including metalloids. Plant aquaporins have been divided into four major subfamilies: plasma membrane intrinsic proteins (PIPs), NOD26-like intrinsic proteins (NIPs), tonoplast intrinsic proteins (TIPs), and small basic intrinsic proteins (SIPs). Various studies have shown that the transport of metalloids including arsenite, antimonite, silicon and boron in plants is facilitated by members of NIP subfamily. ^   In this study, we provided experimental evidences showing that members of rice PIP subfamily are involved in arsenite and boron permeability. RT-PCR analysis of seven OsPIPs; <i>OsPIP1;2, OsPIP1;3, OsPIP2;4, OsPIP2;5, OsPIP2;6, OsPIP2;7</i>, and <i>OsPIP2;8</i> showed that these genes were downregulated under arsenite toxicity in shoots and roots. Whereas, these <i>OsPIP</i> genes were deferentially regulated in shoots and highly induced in roots by boron toxicity. Heterologous expression in <i> Xenopus laevis</i> oocytes showed that <i>OsPIP2;4, OsPIP2;6</i>, and <i>OsPIP2;7</i> significantly increased the transport of arsenite. Expression of OsPIP candidate genes in HD9 yeast strain lacking the metalloids influx and efflux systems resulted in an increased boron sensitivity and accumulation. Overexpression of two OsPIP candidates; <i>OsPIP1;3</i> and <i> OsPIP2;6</i> in <i>Arabidopsis</i> yielded enhanced arsenite and boron tolerance with higher biomass and greater root length compared to wild type plants, however there was no difference in arsenic and boron accumulation in long-term uptake assays. Short duration exposure to AsIII resulted in both active influx and efflux of As in shoots and roots, suggesting a bidirectional transport activity of OsPIPs. Whereas, short-term uptake assay of tracer B (<sup>10</sup>B) in shoots and roots demonstrated increased <sup>10 </sup>B influx in transgenic <i>Arabidopsis</i> lines indicating that these OsPIPs are also involved in mediating B transport in plants. We used RNAi approach to knockdown the expression of <i>OsPIP1;3</i> and <i>OsPIP2;6</i> in rice. We generated RNAi lines for both genes and qRT-PCR analysis showed a significant decrease in the transcript levels for OsPIP1;3 and OsPIP2;6. These RNAi lines will be the subject of future studies.  ^   These OsPIPs genes will be highly useful in developing arsenite and boron tolerant crops for enhanced yield in the areas affected by high As and B toxicity. ^</p>

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<author>Mosa, Kareem A</author>

<source></source>

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<title>Influence of Phosphate on the Adsorption/Desorption of Bovine Serum Albumin on Nano and Bulk Oxide Particles</title>
<link>http://scholarworks.umass.edu/open_access_dissertations/562</link>
<guid isPermaLink="true">http://scholarworks.umass.edu/open_access_dissertations/562</guid>
<pubDate>Thu, 30 Aug 2012 07:32:54 PDT</pubDate>
<description>
	<![CDATA[
	<p>This work consists of four sections: 1) the adsorption behavior of bovine serum albumin (BSA) by three types of oxide nanoparticles (NPs), TiO2 (50 ± 5 nm), SiO2 (30 ± 5nm), and Al2O3 (150 ± 5 nm for α type and 60 ± 5 nm for γ type) in deionized water; 2) phosphate adsorption on these oxide NPs and bulkparticles (BPs); 3) influence of phosphate ions on BSA adsorption; and 4) BSA desorption from oxide NPs in phosphate solution. BPs were also used for comparison with NPs. For BSA adsorption in deionized water, the adsorption maxima on oxide particles are controlled by the surface area and hydrogen content, while the adsorption process is primarily induced by electrostatic interaction, hydrophobic interaction, and ligand exchange between BSA and oxide surfaces. With increasing of hydrogen content, the BSA adsorption mechanism switches from a mainly hydrophobic interaction to hydrogen bonding and ligand exchange. Calculations based on surface area and BSA size, suggest that a multilayer of BSA covers α-Al2O3, but only a single layer surrounds the other oxide particle surfaces. BPs lead to greater conformational change of BSA molecules after their adsorption on the surfaces of oxide particles, although NPs adsorbed more BSA than BPs by weight. For phosphate, e adsorption process is mainly governed by the surface charge of the oxides. Strong electrostatic repulsion can prevent the adsorption of phosphate ions on an oxide surface. Meanwhile, a good linear relationship was observed between surface-normalized BSA adsorption maxima and surface charge of the oxides. For the influence of phosphate ions on BSA adsorption, BSA adsorption is suppressed by phosphate ions, while BSA molecules have no influence on phosphate adsorption. The competition between BSA molecules and phosphate ions is regulated by electrostatic interaction, the hydrogen content of the oxides and oxide surface area (especially micropore surface area). The difference of influence between hydrophobic and hydrophilic interactions on BSA adsorption reduces with the increase of phosphate concentration. Moreover, quantification was employed to calculate the displacing amount of phosphate ions to BSA molecules in competition. The displacing amount of phosphate ions is regulated by micropore surface area, and shows a good linearity with the hydrogen content. For BSA desorption, the BSA desorption hysteresis is observed for SiO2 NPs due to the high aggregation of this type of NPs. The aggregation of NPs can entrap BSA molecules in the closed interstitial spaces, leading to the BSA desorption hysteresis. For α-Al2O3 and γ- Al2O3 NPs, the hysteresis is observed only at low BSA concentration due to the influence of BSA molecules and electrostatic repulsion to the suspension of NPs. For TiO2 NPs, no significant hysteresis is observed because of their low aggregation and strong electrostatic repulsion. Phosphate adsorbed amounts remain unchanged within the adsorption and two-cycle desorption, indicating the entrapped BSA molecules may not bond to the oxide NPs.</p>

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<author>Song, Lei</author>

<source></source>

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<title>Management of Switchgrass for the Production Of Biofuel</title>
<link>http://scholarworks.umass.edu/open_access_dissertations/548</link>
<guid isPermaLink="true">http://scholarworks.umass.edu/open_access_dissertations/548</guid>
<pubDate>Wed, 29 Aug 2012 12:05:42 PDT</pubDate>
<description>
	<![CDATA[
	<p>Switchgrass (Panicum virgatum L.) is a warm-season perennial being considered as a biofuel to meet energy challenges. In Massachusetts, a small state where the price of land is expensive, farmers want to determine if switchgrass can produce sufficient yields for consecutive years to warrant its production. The objective of this study was to determine what harvest management practices affect the vigor and health of switchgrass and which varieties produce the best yields for biofuel production.</p>
<p>Four experiments were conducted from 2009-2012. Twelve varieties were tested to determine their viability in the Massachusetts climate. Five were chosen for further chemical analysis. All varieties were harvested in August (senescence), November (killing frost), and April (early spring). A high yielding variety, Cave-in-Rock, known to grow well in northern latitudes, was chosen for more extensive research. In one experiment, a young stand, three years old, received three nitrogen treatments, was cut at two heights, and was harvested at three different times during the year. A mature stand, seven years old, of the same variety located on conservation land, was harvested three times at two cutting heights. These experiments were done to provide projections on the expected yields over the plant's 10 to 20 year life cycle. In our final experiment Switchgrass was harvested every two weeks from September to November. A caliometer tracked how much energy was present in the dry matter throughout the growing season. Dry matter yield, chemical constituents, and carbohydrate reserves in the below ground tissues were measured as indicator variables to determine the health and quality of yield. Harvest time was the most significant variable observed.</p>

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<author>Gorlitsky, Leryn Elise</author>

<source></source>

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<title>Population dynamics of the Hemlock Woolly Adelgid (Hemiptera: Adelgidae)</title>
<link>http://scholarworks.umass.edu/dissertations/AAI3482653</link>
<guid isPermaLink="true">http://scholarworks.umass.edu/dissertations/AAI3482653</guid>
<pubDate>Mon, 16 Apr 2012 14:14:02 PDT</pubDate>
<description>
	<![CDATA[
	<p> The hemlock woolly adelgid, <i>Adelges tsugae,</i> is an invasive insect from Osaka, Japan threatening populations of eastern hemlock, <i> Tsuga canadensis,</i> and Carolina hemlock, <i>Tsuga caroliniana, </i> in the eastern United States. Previous studies of adelgid population dynamics and hemlock response in the early-1990s suggested that once infested, trees were likely to die within 4 to 6 years; widespread eradication of hemlock throughout the region was expected. However, the vast majority of hemlocks in western Massachusetts are still alive and many are not yet infested, despite the adelgid having been present in the state for 17 years. Many examples of individual trees in Massachusetts harboring adelgid for over ten years have been documented. In order to understand this discrepancy, we conducted detailed lifetable studies of the hemlock woolly adelgid at six locations in Connecticut and Massachusetts from 2004-2008. Adelgid density, fecundity, and survival data as well as temperature and precipitation data were examined to document and understand the apparent stability of adelgid populations in the northeast. These data were also used along with climate projection models to predict the range of suitable habitat for adelgid under two scenarios of carbon emissions through the year 2100.^   In an attempt to regulate adelgid populations, several species of biological control agents have been released, including <i>Laricobius nigrinus</i> Fender (Derodontidae), <i>Sasajiscymnus tsugae</i> Sasaji and McClure (Coccinellidae), and <i>Scymnus ningshanensis</i> Yu and Yao (Coccinellidae). Since few studies have addressed the efficacy of these beetles above the branch level, we conducted an experiment to test their effects on adelgid populations using whole-tree enclosures. These data, in addition to adelgid demography data will be useful in predicting future outbreaks, constructing simulations of adelgid growth and spread, and determining the amount of additional mortality needed from a biological control agent to stabilize adelgid populations.^</p>

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<author>Paradis, Annie F</author>

<source></source>

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<title>Functional characterization of stress associated proteins (SAPS) from arabidopsis</title>
<link>http://scholarworks.umass.edu/dissertations/AAI3482613</link>
<guid isPermaLink="true">http://scholarworks.umass.edu/dissertations/AAI3482613</guid>
<pubDate>Wed, 18 Jan 2012 12:11:27 PST</pubDate>
<description>
	<![CDATA[
	<p> Abiotic stresses such as drought, salt, cold, heat and exposure to toxic metals adversely affect growth and productivity of crop plants and are serious threats to agriculture. Members of Stress Associated Protein (SAP) family in rice have been shown to provide tolerance to multiple abiotic stresses. There are 18 and 14 reported members of SAP family in rice and <i>Arabidopsis, </i> respectively. These SAPs contain A20, AN1, or both A20/AN1 zinc finger domains at the N- or C-terminus. Some members of SAP family proteins also contain extra Cys2-His2 RING motifs on the C-terminus.^   We describe here the functional characterization of two novel SAP genes, <i> AtSAP10 </i>and <i>AtSAP11,</i> from <i>Arabidopsis thaliana </i> ecotype Columbia. <i>AtSAP10 </i>gene contains an A20 and AN1 zinc-finger domain at the N- and C-terminal, respectively. <i> Arabidopsis SAP10</i> showed differential regulation by various abiotic stresses such as heavy metals and metalloids (Ni, Cd, Mn, Zn, and As), high and low temperatures, cold, and ABA. Overexpression of AtSAP10 in <i> Arabidopsis </i>conferred strong tolerance to heavy metals such as Ni, Mn, and Zn and to high temperature stress. AtSAP10 transgenic plants under these stress conditions grew green and healthy, attained several-fold more biomass, and had longer roots as compared to wild type plants. Further, while these transgenic plants accumulated significantly greater amounts of Ni and Mn in both shoots and root tissues, there was no significant difference in the accumulation of Zn. <i>AtSAP10 </i>promoter-GUS fusion studies revealed a root and floral organ-specific expression of AtSAP10. Overexpression of AtSAP10-GFP fusion protein showed the localization in both nucleus and cytoplasm.^   A second gene from AtSAP family, <i>AtSAP11,</i> contains two AN1 zinc finger domains at N-terminal and two C2H2 zinc finger domains at C-terminus. <i>Arabidopsis SAP11</i> showed differential regulation by various abiotic stresses such as heavy metals and metalloids (As, Cd and Zn), high and low temperatures, cold, and salt. Overexpression of AtSAP11 in <i>Arabidopsis </i>conferred moderate tolerance to heavy metals As and Zn and slightly enhanced tolerance to drought stress. AtSAP11 overexpression plants did not accumulate significantly higher amounts arsenic in shoots or roots. <i>AtSAP11 </i>promoter-GUS fusion studies revealed a floral organ-specific and fruit specific expression of AtSAP11. AtSAP11-GFP fusion showed an ER like localization of the fusion protein. Thus these results showed that AtSAP10 and AtSAP11 are potentially useful candidate genes for engineering tolerance to heavy metals and to abiotic stress in cultivated plants. ^</p>

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<author>Dixit, Anirudha R</author>

<source></source>

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<title>Armillaria in Massachusetts Forests: Ecology, Species Distribution, and Population Structure, with an Emphasis on Mixed Oak Forests</title>
<link>http://scholarworks.umass.edu/open_access_dissertations/402</link>
<guid isPermaLink="true">http://scholarworks.umass.edu/open_access_dissertations/402</guid>
<pubDate>Fri, 19 Aug 2011 12:43:13 PDT</pubDate>
<description>
	<![CDATA[
	<p>The ecology, species distribution, and population structure of Armillaria was investigated in the forests of Massachusetts. From 64 plots at 16 sites, 640 isolates of Armillaria were collected from six forest types (northern hardwoods, mixed oak, pitch pine, white pine, white pine/mixed oak, and eastern hemlock). Armillaria gallica proved to be the most abundant species, making up 316/640 (52%) of all isolations. This was followed by A. solidipes (219/640; 34%), A. mellea (46/640; 7%), A. calvescens (36/640; 6%), A. gemina (16/640; 3%), and A. sinapina (7/640; 1%). Armillaria gallica was routinely encountered causing significant decay of the lower bole on living hardwood hosts, especially oaks. The population structure of 153 isolates of A. gallica collected from mixed oak forests was investigated using amplified fragment length polymorphisms (AFLPs). From a total sampling area of 4.51 ha, 38 AFLP genotypes were discovered, yielding a figure of eight genets per hectare with the average A. gallica genet occupying 0.13 ha. When the effects of hydrolyzable tannins on in vitro growth were compared between A. calvescens and A. gallica, it was A. gallica that appeared better at oxidizing and metabolizing commercial tannins (tannic acid and gallic acid) along with black oak root bark extracts. This was determined through measurements of colony area and dry biomass, and suggests that A. gallica may be a better adapted pathogen of oak. In order to more accurately distinguish between isolates of A. calvescens and A. gallica, a three-gene phylogeny was reconstructed, using partial sequences of the elongation factor 1-alpha (tef1), RNA polymerase II (rpb2) and nuclear large subunit (nLSU) genes. After comparing 12 isolates each of A. calvescens and A. gallica that originated from across northeastern North America, only the tef1 gene could accurately distinguish these two species. Five single nucleotide polymorphisms were present between the two species and maximum likelihood and maximum parsimony methods grouped A. calvescens and A. gallica into monophyletic clades.</p>

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<author>Brazee, Nicholas Justin</author>

<source></source>

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<title>Developing an Efficient Cover Cropping System for Maximum Nitrogen Recovery in Massachusetts</title>
<link>http://scholarworks.umass.edu/open_access_dissertations/394</link>
<guid isPermaLink="true">http://scholarworks.umass.edu/open_access_dissertations/394</guid>
<pubDate>Fri, 19 Aug 2011 12:42:36 PDT</pubDate>
<description>
	<![CDATA[
	<p>Time of planting plays a critical role in nitrogen (N) uptake by rye cover crop (CC). Even a few days of delay in planting can severely decrease CC performance. Evaluating the amount of N accumulation related to time of planting is critical to the farmer who has to optimize the winter rye planting date based on completion of corn harvest, suitable weather conditions and time availability for fall manure application. Winter rye cover crop was planted at 6 planting dates in fall from mid August to early October at weekly intervals from 2004 to 2009.</p>
<p>The results suggest that delay from critical planting date (CPD) will decrease rye N uptake dramatically. Suggested CPDs for northwest parts of Massachusetts are not applicable because they are too early (third to fourth week of August). CPDs for central parts of the State are from first to second week of September. Farmers in these zones can take advantage of cover crop by a better time management and planting no later than vii CPD. In Eastern areas of Massachusetts CPD is the third week of September. By evaluating the effect of planting date on rye growth and N accumulation throughout the State, this model provides a powerful decision making tool for increasing N recovery and reducing nutrient leaching.</p>
<p>Sixteen units of cost effective and accurate automated lysimeters were designed and installed to measure post-harvest nitrate leaching from a rye cover crop field during the falls and winters of 2007 to 2009. The electronic system was designed to monitor soil tension and apply the equal amount of suction to the sampling media. Hourly data from soil tension and vacuum applied to the system were collected and stored by each unit. A safety system was designed for protecting vacuum pump against unexpected major vacuum leakage events. The controller can be easily reprogrammed for different performance strategies. Other major parts of lysimeter included the power supply systems, vacuum pump, vacuum tanks, sampling jars, suction cups and plates, and electronic valves. The electronic system showed a very reliable and accurate performance in the field condition.</p>

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<author>Farsad, Ali</author>

<source></source>

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<title>Bacterial Toxicity of Oxide Nanoparticles and Their Effects on Bacterial Surface Biomolecules</title>
<link>http://scholarworks.umass.edu/open_access_dissertations/386</link>
<guid isPermaLink="true">http://scholarworks.umass.edu/open_access_dissertations/386</guid>
<pubDate>Fri, 19 Aug 2011 12:42:01 PDT</pubDate>
<description>
	<![CDATA[
	<p>Toxicity of nano-scaled Al2O3, SiO2, TiO2 and ZnO to bacteria (Bacillus subtilis, Escherichia coli and Pseudomonas fluorescens) was examined and compared to that of their respective bulk (micro-scaled) counterparts. All nanoparticles (NPs) but TiO2 showed higher toxicity than their bulk counterparts. Toxicity of released metal ions was differentiated from that of the oxide particles. ZnO was the most toxic among the three NPs, causing 100% mortality to the three tested bacteria. TEM images showed attachment of NPs to the bacteria, suggesting that the toxicity was affected by bacterial attachment.</p>
<p>The effects of oxide NPs on bacteria cells and bacterial surface biomolecules were studied by FTIR spectroscopy to provide a better understanding of their cytotoxicity. Lipopolysaccharide (LPS) and lipoteichoic acid could bind to oxide NPs through hydrogen bonding and ligand exchange, but the cytotoxicity of NPs seemed largely related to the function-involved or structural changes to proteins and phospholipids. The three NPs decreased the intensity ratio of β-sheets/α-helices, indicating protein structure change, which may affect cell physiological activities. The phosphodiester bond of L-α- Phosphatidyl-ethanolamine (PE) was broken by ZnO NPs, forming phosphate monoesters and resulting in the highly disordered alkyl chain. Such damage to phospholipid molecular structure may lead to membrane rupture and cell leaking, which is consistent with the fact that ZnO is the most toxic of the three NPs.</p>
<p>LPS and PE are amphiphilic biomolecules that are major constituents of the outer membrane of Gram-negative bacteria. Their micelles and vesicles were studied as model cell membranes to evaluate NP effects on membrane construction. The adsorption of polysaccharides on Al2O3 and TiO2 NPs dispersed LPS vesicles and micelles. LPS coated Al2O3 NPs, while it caused the aggregation of TiO2 NPs according to atom force microscopy images. Desorption from the two NPs was slow due to the firm hydrogen bonding. For PE, Al2O3 NPs induced large multilamillar vesicles, while ZnO NP converted vesicles to tiny aggregates due to molecular structure breakup. PE stability in solution was disturbed by adding NPs, but its stability was enhanced by increasing pH. The electrostatic force was the determining factor for the vesicle stability.</p>

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<author>Jiang, Wei</author>

<source></source>

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<title>Influence of natural organic matter (NOM) and synthetic polyelectrolytes on colloidal behavior of metal oxide nanoparticles</title>
<link>http://scholarworks.umass.edu/dissertations/AAI3409578</link>
<guid isPermaLink="true">http://scholarworks.umass.edu/dissertations/AAI3409578</guid>
<pubDate>Wed, 25 Aug 2010 11:52:24 PDT</pubDate>
<description>
	<![CDATA[
	<p> The colloidal behavior of engineered nanomaterials exposed in an aquatic environment may significantly influence their bioavailability as well as toxicity to different species. Natural organic matter (NOM) is one of the major colloidal materials ubiquitous in the environment with significant structural heterogeneity. Therefore, role of NOM molecules on environmental fate of these engineered NPs needs to be addressed. Colloidal behavior of aluminum (Al<sub>2</sub>O<sub> 3</sub>) and magnetic iron oxide (γFe<sub>2</sub>O<sub>3</sub>) NPs was studied in the presence of structurally different HAs and synthetic polyacrylic acids (PAAs). The conformation behavior of the adsorobed NOM/polyelectrolyte under specific solution conditions were determined with dynamic light scattering, atomic force microscopy measurements.^   Al<sub>2</sub>O<sub>3</sub> NPs followed the classical DLVO model of colloidal behavior in their pristine state. However, a significant deviation from the classical DLVO model was observed when these NPs were coated with structurally different HAs. Low polar, high molecular weight HA fractions showed much stronger stabilization against Ca<sup>2+</sup> induced aggregation. Previously, we observed that these low polar, high molecular weight fractions strongly destabilized the NP suspension when added in a small quantity. A significant transformation in suspension stability was observed possibly due to steric effect of these adsorbed HAs.^   The colloidal behavior of PAA/NOM coated ferrimagnetic γFe<sub> 2</sub>O<sub>3</sub> NPs were investigated. Pure γFe<sub>2</sub>O<sub> 3</sub> NPs were extremely unstable in aqueous solution but a significant enhancement in colloidal stability was observed after coating with polyelectrolytes/NOM. The steric as well as electrostatic stabilization introduced by the polyelectrolyte coating strongly dictated the colloidal stability. The alteration of electrosteric stabilization mechanisms by pH-induced conformation change profoundly influences the colloidal stability. Atomic force microscopy (AFM) study revealed a highly stretched conformation of the HA molecular chains adsorbed on γFe<sub> 2</sub>O<sub>3</sub> NP surface with increasing pH from 5 to 9 which enhanced the colloidal stability trough long range electrosteric stabilization. The depletion of the polyelectrolytes during dilution of the suspension in the acidic solution conditions and in the presence of Na<sup>+</sup> or Ca<sup> 2+</sup> decreased the colloidal stability. The conformation of the polyelectrolytes adsorbed on the NP surface altered significantly as a function of substrate surface charge as viewed from the AFM imaging.^</p>

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<author>Ghosh, Saikat</author>

<source></source>

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