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Orientador: Iracema Helena Schoenlein-Crusius / Banca: Carmen Lidia Amorim Pires-Zottarelli / Banca: Sandra Farto Botelho Trufem / Banca: Dejanira de Franceschi de Angelis / Banca: Carlos Renato Corso / Resumo: Em solo contaminado com metais pesados na região do pólo cerâmico do município de Santa Gertrudes, Estado de São Paulo, Brasil, foi realizado o levantamento taxonômico de fungos da ordem Mucorales (Zygomycota) utilizando-se o método da placa-de-solo, modificado pela aplicação de uma suspensão de solo (10%, p v-1) sobre malte agar (2%, p v-1) acrescido de Pb(NO3)2 ou Zn(NO3)2 nas concentrações de 0 (controle), 100, 200, 500 e 1000 mg L-1. As identificações e descrições taxonômicas foram realizadas utilizando-se SMA (synthetic Mucor agar), sendo obtidos os táxons: Absidia cylindrospora v. cylindrospora Hesselt. & Ellis, Cunninghamella phaeospora Boedijn, Mucor circinelloides Tiegh. f. circinelloides, M. circinelloides Tiegh. f. lusitanicus (Bruderl.) Schipper, M. circinelloides Tiegh. f. janssenii (Lendn.) Schipper, Mucor hiemalis Wehmer f. hiemalis, M. hiemalis Wehmer f. luteus (Linnem.) Schipper, Mucor racemosus Fresen. f. racemosus, Rhizopus oryzae Went & Prins. Geerl., Zygorrhynchus moelleri Vuill. e Mucor bainieri Mehrotra & Baijal, que é citado pela primeira vez para o Brasil. Análises químicas de amostras de solo coletadas em quatro locais na área estudada confirmaram a contaminação severa por metais pesados em alguns dos locais, sendo que comparações entre o número de táxons obtidos no presente estudo com os dados de literatura permitiram concluir que houve prejuízo à diversidade de fungos na região. As biomassas secas e pulverizadas (2 g L-1) de Mucor hiemalis f. hiemalis (SPC 2040) e de Mucor hiemalis f. luteus (SPC 2044) foram colocadas em contato, sob agitação a 120 rpm por 14 h, com soluções aquosas (pH 4) de Pb(NO3)2 e Zn(NO3)2 nas concentrações de 0,06, 0,13 e 0,17 mM e de 0,08, 0,16 e 0,23 mM, respectivamente, sendo comparadas ao carvão ativado (CA), utilizado como material adsorvente de referência / Abstract: In a heavy metal contaminated soil at ceramic pole of Santa Gertrudes region, São Paulo State, Brazil, a taxonomic survey of fungi of the order Mucorales (Zygomycota) have been done using the soil plate method, modified for a soil suspension (10%, p v-1) application on malt agar (2%, p v-1) added with Pb(NO3)2 or Zn(NO3)2 at 0 (control), 100, 200, 500 and 1000 mg L-1 concentrations. Taxonomic identifications and descriptions have been done with SMA (synthetic Mucor agar), obtaining the taxa: Absidia cylindrospora v. cylindrospora Hesselt. & Ellis, Cunninghamella phaeospora Boedijn, Mucor circinelloides Tiegh. f. circinelloides, M. circinelloides Tiegh. f. lusitanicus (Bruderl.) Schipper, M. circinelloides Tiegh. f. janssenii (Lendn.) Schipper, Mucor hiemalis Wehmer f. hiemalis, M. hiemalis Wehmer f. luteus (Linnem.) Schipper, Mucor racemosus Fresen. f. racemosus, Rhizopus oryzae Went & Prins. Geerl., Zygorrhynchus moelleri Vuill. and Mucor bainieri Mehrotra & Baijal, that is cited first time for Brazil. Chemical analyses of soil samples taken from four sites in the studied area confirm a severe contamination of heavy metals in some of the sites, and comparisons between taxa numbers obtained in the present study with literature data allowed conclude that there was fungal diversity disturbance in the region. The dry and grounded biomasses (2 g L-1) of Mucor hiemalis f. hiemalis (SPC 2040) and Mucor hiemalis f. luteus (SPC 2044) was kept in contact, under agitation at 120 rpm during 14 h, with aqueous solutions (pH 4) of Pb(NO3)2 and Zn(NO3)2 at 0.06, 0.13, 0.17 mM and 0.08, 0.16, 0.23 mM concentrations, respectively, being compared with activated charcoal (AC) as the reference adsorbent. The percentages amounts of metals removed from solutions, express by q% index, had presented the following adsorption sequences: AC > SPC 2044 > SPC 2040 for Pb and AC > SPC 2040 > SPC 2044 for Zn / Doutor

<p>Trafik utgör en stor föroreningskälla av tungmetaller i vägnära jordar och särskilt är det koppar (Cu), bly (Pb) och zink (Zn) som associeras med fordonstrafik. I ett historiskt perspektiv härrör blyutsläpp främst från bränsleförbränning, medan kopparemissioner (i första hand från slitage av bromsbelägg) och zinkutsläpp (från däck) från trafik står för så mycket som hälften av det urbana utsläppet av koppar och zink till omgivningen.</p><p>Koppar-, bly- och zinkkoncentrationer i vägnära jord och sediment undersöktes inom avrinningsområdet för Grand River North West i Mauritius. Eftersom totalmetall utgör en dålig indikator på den mängd metall som finns potentiellt tillgänglig för biota användes extraktion med hjälp av 0.5 M HCl tillsammans med totalkoncentrationer.</p><p>Den rumsliga variationen längsmed transekt vinkelrätt mot vägar undersöktes liksom variationen med djupet. Observerade kopparkoncentrationer var jämförbara med bakgrundsnivåer. Till skillnad från Cu var koncentrationer av Pb och Zn förhöjda i den omedelbara närheten till vägar med relativt stor trafikintensitet, men halterna minskade snabbt med avståndet. Resultat från platserna för jordreferenser visar på storskalig förorening av Pb på ön. Uppmätta kopparkoncentrationer kunde inte knytas till trafikens påverkan.</p><p>Vid regn kan metaller som finns i förorenat vägdamm och förorenad jord övergå till löslig form, eller sköljas bort i partikulär form, och transporteras till närliggande vattendrag. I Mauritius är det här av speciell vikt eftersom flodsediment till slut kommer att deponeras i de känsliga kustområdena som omger ön. Dock tyder inte resultaten på förhöjda metallhalter i sediment nära de studerade vägarna.</p><p>Även om erhållna resultat av Cu inte visar på någon förhöjning och zonen med hög förorening av Pb och Zn är relativt smal, är det angeläget att följa utvecklingen eftersom antalet fordon växer snabbt i Mauritius, vilket kan förändra dagens situation och ge upphov till större miljöpåverkan. För att undvika eventuella ekologiska skador är det därför av stor vikt att i fortsättningen övervaka situationen längs landets vägar.</p> / <p>Traffic has been identified as a significant heavy metal polluter of roadside soils, and copper (Cu), lead (Pb) and zinc (Zn) in particular are associated with road travel. In a historic perspective, the Pb contribution from anthropogenic sources to nature has predominantly been a result of fuel combustion. There are indications that Cu (mainly through braking system) and Zn (emissions from tires) released from traffic give rise to as much as half of the total urban contribution of copper and zinc to the environment.</p><p>Concentrations of Cu, Pb and Zn in roadside soils and sediment have been determined at selected roads within the Grand River North West watershed in Mauritius. As total metal concentrations are not a suitable indicator of the metal concentrations that are potentially available to biota, metals extractable in 0.5 M HCl have been determined along with total concentrations. The spatial variation in metal concentration along soil transects perpendicular to roads were investigated, as was the variation with depth.</p><p>Observed Pb and Zn concentrations exhibited elevated levels in topsoil in the immediate vicinity of roads with relatively large traffic densities, but the decrease in concentration with distance was rapid. Results from soil reference sites pointed to a large scale Pb pollution on the island. In comparison, observed Cu concentrations could not be assigned any influence from traffic at the selected study sites.</p><p>In the event of rain, metals contained in polluted road dust and soil may be released into soluble form, or flushed from roadways as particulate matter, and transported to nearby water courses. In Mauritius, this is of particular importance as sediment in rivers eventually may be deposited in the sensitive coastal areas of the island. However, results do not indicate that there were any elevated levels of heavy metals in sediment close to roads that were investigated in this study.</p><p>Although Cu concentrations in roadside soils did not show any enrichment and the zone of elevated Pb and Zn concentrations was not wide, there is a concern that the continuing rapid increase in the number of vehicles in Mauritius will change the situation, possibly resulting in greater impact on the surrounding environment. Hence, in order to avoid any ecological damage, it is desirable to continue monitoring the situation along highways in the country.</p>

The Australian and New Zealand Environment and Conservation Council (ANZECC) and the Agriculture and Resource Management Council of Australia and New Zealand (ARMCANZ) have announced that the 1997 review of the Australian Water Quality Guidelines will include for the first time, consideration of sediment quality guidelines. For this reason, it is timely to review the methods for establishing such guidelines, and the manner in which they could be used in managing the quality of sediments in Australian rivers, lakes and drainage systems. In this thesis, the problem of the development of sediment quality guidelines is introduced and basic questions relating to the development of such guidelines are addressed. The importance of sediment monitoring and sediment quality assessment in aquatic ecosystem management is demonstrated, and the role of sediment quality guidelines in the process of sediment quality assessment is discussed. The arguments considered in this thesis are illustrated by specific reference to the setting and use of sediment quality guidelines for heavy metal contamination. A number of physico-chemical factors (grain size distribution, pH, redox potential, alkalinity and hardness, salinity, organic matter) can affect the bioavailability and toxicity of contaminants in sediments, and these factors may vary spatially and temporally within and between sediment deposits. Changes in physico-chemical conditions as a result of natural or anthropogenic processes may lead to major changes in bioavailability of sediment contaminants. The variability of these physico-chemical factors has ramifications for the way in which sediment quality guidelines are derived and used. Factors affecting the way in which toxicity is measured (test species chosen, toxicological end-point measured, duration of test relative to life-cycle), and toxicity data is interpreted, are also important to the development of useful sediment quality guidelines. All of these factors must be taken into account in deriving sediment quality guidelines for Australian conditions. The large number of factors affecting the sensitivity and efficiency of sediment quality guidelines means that a simple set of numerical guidelines, as has been used in the past, is not appropriate. A multi-step assessment procedure will be required. Methods of setting sediment quality guidelines that have been used by authorities in overseas jurisdictions were reviewed. Advantages and disadvantages of the various methods were compared. None of the methods used overseas has been shown to be applicable to Australian conditions. In the absence of a suitable method for deriving Australian sediment quality guidelines in the short term, the adoption of the Canadian Interim Sediment Quality Guidelines as interim sediment quality guidelines for Australia is recommended. Sediment quality guidelines need to be viewed in the context of the overall environmental management process, of which they form an integral part. The policy background to environmental management in Australia, and the management frameworks that have been put in place to implement the policy, are outlined. The AS/NZS/ISO 14000 series of standards for environmental management systems provides a framework which is consistent with the principles and objectives of environmental management in Australia. It therefore provides an appropriate framework within which to develop and use sediment quality guidelines. Within the broad AS/NZS/ISO 14000 policy, a framework for the development and use of sediment quality guidelines is proposed, which will provide a technically and legally defensible basis for the management of aquatic sediments in Australia, in the short term and long term. The proposed framework involves the setting of Interim Sediment Quality Guidelines for Australia, based on the best scientific knowledge currently available. The framework recognises that the factors affecting the bioavailability and toxicity of sediment contaminants are complex, and that the current level of knowledge of sediment processes is incomplete. Therefore, a conservative approach to setting guidelines is taken, and a highly sensitive guideline based on that used in Canada, is proposed. The framework further recognises that this approach will lead to over protection of the environment in some cases, so a "Decision Tree" approach is taken. The "decision tree" allows the consideration of more complex interactions than can be incorporated into simple numeric guidelines, while attempting to simplify the assessment process. In keeping with the ISO 14000 series of standards for environmental management, the framework also explicitly includes steps designed to ensure that monitoring data are regularly collated, and analysed, and where necessary, guidelines are able to be updated in light of new knowledge gleaned from the review process. The proposed framework is appropriate to, and supportive of, the principles of environmental management as set out in Australian Government policy documents, inter governmental and international agreements, and legislation. It provides a basis for the on-going collection of data suited to increasing our understanding of the factors influencing the behaviour of contaminants in sediments, and thereby lead to continual improvement in sediment quality guidelines for use in Australian conditions.

Trafik utgör en stor föroreningskälla av tungmetaller i vägnära jordar och särskilt är det koppar (Cu), bly (Pb) och zink (Zn) som associeras med fordonstrafik. I ett historiskt perspektiv härrör blyutsläpp främst från bränsleförbränning, medan kopparemissioner (i första hand från slitage av bromsbelägg) och zinkutsläpp (från däck) från trafik står för så mycket som hälften av det urbana utsläppet av koppar och zink till omgivningen. Koppar-, bly- och zinkkoncentrationer i vägnära jord och sediment undersöktes inom avrinningsområdet för Grand River North West i Mauritius. Eftersom totalmetall utgör en dålig indikator på den mängd metall som finns potentiellt tillgänglig för biota användes extraktion med hjälp av 0.5 M HCl tillsammans med totalkoncentrationer. Den rumsliga variationen längsmed transekt vinkelrätt mot vägar undersöktes liksom variationen med djupet. Observerade kopparkoncentrationer var jämförbara med bakgrundsnivåer. Till skillnad från Cu var koncentrationer av Pb och Zn förhöjda i den omedelbara närheten till vägar med relativt stor trafikintensitet, men halterna minskade snabbt med avståndet. Resultat från platserna för jordreferenser visar på storskalig förorening av Pb på ön. Uppmätta kopparkoncentrationer kunde inte knytas till trafikens påverkan. Vid regn kan metaller som finns i förorenat vägdamm och förorenad jord övergå till löslig form, eller sköljas bort i partikulär form, och transporteras till närliggande vattendrag. I Mauritius är det här av speciell vikt eftersom flodsediment till slut kommer att deponeras i de känsliga kustområdena som omger ön. Dock tyder inte resultaten på förhöjda metallhalter i sediment nära de studerade vägarna. Även om erhållna resultat av Cu inte visar på någon förhöjning och zonen med hög förorening av Pb och Zn är relativt smal, är det angeläget att följa utvecklingen eftersom antalet fordon växer snabbt i Mauritius, vilket kan förändra dagens situation och ge upphov till större miljöpåverkan. För att undvika eventuella ekologiska skador är det därför av stor vikt att i fortsättningen övervaka situationen längs landets vägar. / Traffic has been identified as a significant heavy metal polluter of roadside soils, and copper (Cu), lead (Pb) and zinc (Zn) in particular are associated with road travel. In a historic perspective, the Pb contribution from anthropogenic sources to nature has predominantly been a result of fuel combustion. There are indications that Cu (mainly through braking system) and Zn (emissions from tires) released from traffic give rise to as much as half of the total urban contribution of copper and zinc to the environment. Concentrations of Cu, Pb and Zn in roadside soils and sediment have been determined at selected roads within the Grand River North West watershed in Mauritius. As total metal concentrations are not a suitable indicator of the metal concentrations that are potentially available to biota, metals extractable in 0.5 M HCl have been determined along with total concentrations. The spatial variation in metal concentration along soil transects perpendicular to roads were investigated, as was the variation with depth. Observed Pb and Zn concentrations exhibited elevated levels in topsoil in the immediate vicinity of roads with relatively large traffic densities, but the decrease in concentration with distance was rapid. Results from soil reference sites pointed to a large scale Pb pollution on the island. In comparison, observed Cu concentrations could not be assigned any influence from traffic at the selected study sites. In the event of rain, metals contained in polluted road dust and soil may be released into soluble form, or flushed from roadways as particulate matter, and transported to nearby water courses. In Mauritius, this is of particular importance as sediment in rivers eventually may be deposited in the sensitive coastal areas of the island. However, results do not indicate that there were any elevated levels of heavy metals in sediment close to roads that were investigated in this study. Although Cu concentrations in roadside soils did not show any enrichment and the zone of elevated Pb and Zn concentrations was not wide, there is a concern that the continuing rapid increase in the number of vehicles in Mauritius will change the situation, possibly resulting in greater impact on the surrounding environment. Hence, in order to avoid any ecological damage, it is desirable to continue monitoring the situation along highways in the country.

Rivers all around the world have become increasingly polluted with heavy metals, largely due to industrialization and urbanization. Organisms exposed to high concentrations of heavy metals have shown evidence of biotoxicity and physical deformities. With biomagnification in mind, the possibility that this contamination may soon directly affect humans is a real concern, and policies in manufacturing industries worldwide may have to be reformed. In this study, we measured the concentrations of arsenic (As), cadmium (Cd), chromium (Cr), copper (Cu), nickel (Ni), and lead (Pb) in the Hatillo River and compared these values to those measured in the Tarcoles River, a highly polluted river, and Terciopelo Creek, a relatively clean river. The results showed that the Hatillo River had significantly lower levels of most detected heavy metals than both the Tarcoles and Terciopelo. Overall, sediments in all rivers showed high levels of heavy metal content--especially in chromium, copper, nickel, and lead--which could build up and affect organisms over a long period of time.

Food production in urban areas has been conducted worldwide as a subsistence strategy and source of income. Recently, however, it is recognized that urban agriculture has the potential to contribute to the development of sustainable urban environments. This study examines the benefits of urban food production in North American cities, as well as focusing on some of the critical barriers to its widespread expansion and acceptance. It also explores the potential for contamination of produce from the ambient atmosphere in mid-sized urban centres. Through interviewing nine urban farmers and one urban planner, in the city of Victoria, British Columbia, I documented each producer’s knowledge of the benefits and limitations associated with urban food production. Each interviewee impressed upon me the numerous benefits that can be accrued through the practice of urban agriculture, but they also painted a picture of the struggles that urban farmers face. Issues identified included: a real and perceived risk of contamination, problems with land ownership and access, and lack of meaningful support for urban farmers. Although urban agriculture has been accepted in principle by the City of Victoria and other Canadian cities, there are many challenges that must be overcome for urban food production to truly produce a viable, sustained food system. A coordinated, comprehensive government policy for involvement in the urban food system is critical to effectively addressing urban food issues. Investigations of heavy metal levels in lettuce (Lactuca sativa) grown in sampling sites across an urban/rural gradient showed that atmospheric contamination by heavy metals is greatest at urban sites, but also affects residential and rural sites. Sampling site types included: a control area (rural farms and properties outside of Victoria); residential sites (yards in residential neighbourhoods in the City of Victoria); and, industrial/business sites (heavily trafficked and industrialized areas in downtown Victoria). Site types were intended to reflect areas perceived as safe, probably safe, and probably not safe, and were selected based on expert opinion and land use. Results indicate that caution should be exercised in growing leafy greens at downtown sites, and that growing food in most residential neighbourhoods and green spaces is typically no worse than growing greens in rural Victoria. In fact, due to the proximity of urban agriculture to the market, growing food locally eliminates the need for transportation and extra processing; reducing the extra exposure crops otherwise might face during these phases. Urban food production requires the support of communities and governments in order to contribute to both urban food security and urban sustainability. The City of Victoria has started on a path to ensuring that this food system receives the required support, but it requires concerted effort and action. Further research into urban food systems is necessary to ensure that urban food production is able to become a viable, sustained food system. / Graduate

Made available in DSpace on 2014-06-11T19:32:55Z (GMT). No. of bitstreams: 0 Previous issue date: 2006-12-05Bitstream added on 2014-06-13T18:44:34Z : No. of bitstreams: 1 souza_ji_dr_rcla.pdf: 1254068 bytes, checksum: 64378d1c217e577afa6ca9eebcf6200f (MD5) / Em solo contaminado com metais pesados na região do pólo cerâmico do município de Santa Gertrudes, Estado de São Paulo, Brasil, foi realizado o levantamento taxonômico de fungos da ordem Mucorales (Zygomycota) utilizando-se o método da placa-de-solo, modificado pela aplicação de uma suspensão de solo (10%, p v-1) sobre malte agar (2%, p v-1) acrescido de Pb(NO3)2 ou Zn(NO3)2 nas concentrações de 0 (controle), 100, 200, 500 e 1000 mg L-1. As identificações e descrições taxonômicas foram realizadas utilizando-se SMA (synthetic Mucor agar), sendo obtidos os táxons: Absidia cylindrospora v. cylindrospora Hesselt. & Ellis, Cunninghamella phaeospora Boedijn, Mucor circinelloides Tiegh. f. circinelloides, M. circinelloides Tiegh. f. lusitanicus (Bruderl.) Schipper, M. circinelloides Tiegh. f. janssenii (Lendn.) Schipper, Mucor hiemalis Wehmer f. hiemalis, M. hiemalis Wehmer f. luteus (Linnem.) Schipper, Mucor racemosus Fresen. f. racemosus, Rhizopus oryzae Went & Prins. Geerl., Zygorrhynchus moelleri Vuill. e Mucor bainieri Mehrotra & Baijal, que é citado pela primeira vez para o Brasil. Análises químicas de amostras de solo coletadas em quatro locais na área estudada confirmaram a contaminação severa por metais pesados em alguns dos locais, sendo que comparações entre o número de táxons obtidos no presente estudo com os dados de literatura permitiram concluir que houve prejuízo à diversidade de fungos na região. As biomassas secas e pulverizadas (2 g L-1) de Mucor hiemalis f. hiemalis (SPC 2040) e de Mucor hiemalis f. luteus (SPC 2044) foram colocadas em contato, sob agitação a 120 rpm por 14 h, com soluções aquosas (pH 4) de Pb(NO3)2 e Zn(NO3)2 nas concentrações de 0,06, 0,13 e 0,17 mM e de 0,08, 0,16 e 0,23 mM, respectivamente, sendo comparadas ao carvão ativado (CA), utilizado como material adsorvente de referência. / In a heavy metal contaminated soil at ceramic pole of Santa Gertrudes region, São Paulo State, Brazil, a taxonomic survey of fungi of the order Mucorales (Zygomycota) have been done using the soil plate method, modified for a soil suspension (10%, p v-1) application on malt agar (2%, p v-1) added with Pb(NO3)2 or Zn(NO3)2 at 0 (control), 100, 200, 500 and 1000 mg L-1 concentrations. Taxonomic identifications and descriptions have been done with SMA (synthetic Mucor agar), obtaining the taxa: Absidia cylindrospora v. cylindrospora Hesselt. & Ellis, Cunninghamella phaeospora Boedijn, Mucor circinelloides Tiegh. f. circinelloides, M. circinelloides Tiegh. f. lusitanicus (Bruderl.) Schipper, M. circinelloides Tiegh. f. janssenii (Lendn.) Schipper, Mucor hiemalis Wehmer f. hiemalis, M. hiemalis Wehmer f. luteus (Linnem.) Schipper, Mucor racemosus Fresen. f. racemosus, Rhizopus oryzae Went & Prins. Geerl., Zygorrhynchus moelleri Vuill. and Mucor bainieri Mehrotra & Baijal, that is cited first time for Brazil. Chemical analyses of soil samples taken from four sites in the studied area confirm a severe contamination of heavy metals in some of the sites, and comparisons between taxa numbers obtained in the present study with literature data allowed conclude that there was fungal diversity disturbance in the region. The dry and grounded biomasses (2 g L-1) of Mucor hiemalis f. hiemalis (SPC 2040) and Mucor hiemalis f. luteus (SPC 2044) was kept in contact, under agitation at 120 rpm during 14 h, with aqueous solutions (pH 4) of Pb(NO3)2 and Zn(NO3)2 at 0.06, 0.13, 0.17 mM and 0.08, 0.16, 0.23 mM concentrations, respectively, being compared with activated charcoal (AC) as the reference adsorbent. The percentages amounts of metals removed from solutions, express by q% index, had presented the following adsorption sequences: AC > SPC 2044 > SPC 2040 for Pb and AC > SPC 2040 > SPC 2044 for Zn.