<p>Fly ash and AMD samples were characterised by standard analytical methods for selection of the test materials. Active treatment by means of mixing fly ash with AMD in beakers and a large tank at pre-determined ratios have shown that fly ash is capable of neutralising AMD and increasing the pH beyond neutral values, which optimises the removal of heavy metals and ions. The trend was: the more fly ash added the quicker was the reaction time and higher the pH values achieved. Iron was reduced by as much 99 % in beaker scale experiments via Fe(OH)3 precipitation at pH values &gt / 4.0. A 99 % decrease in aluminium concentration was observed which was attributed to the precipitation of primarily gibbsite and various other mineral phases at pH values &gt / 5.5. As the pH increases, sulphate is adsorbed via Fe(OH)3 and gypsum precipitation at elevated pH. Sulphate attenuation with fly ash was excellent, achieving 98 % attenuation with beaker scale experiments and 1:1 fly ash:AMD ratio. Sulphate attenuation with fly ash was comparable to membrane and ion exchange systems and exceeded the performance of limestone treatment. Except for the larger volumes of fly ash needed to neutralise the AMD, fly ash proved to be a feasible and cost efficient alternative to limestone treatment. Fly ash produced competing results to limestone concerning acidity removal and sulphate attenuation. The comparison highlighted the advantages of utilising fly ash in comparison to limestone and demonstrated its cost effectiveness. The results of this study have shown that fly ash could be successfully applied for the neutralisation of acid mine drainage (AMD) and effectively attenuate the sulphate load in the treated water. The critical parameters to this technology are the variations of chemical composition and mineralogy of fly ash, which could influence the pH, contact time of the neutralisation reaction, and the same is true if the AMD quality varies.</p>

Acid mine drainage (AMD) is a significant environmental issue worldwide, which often causes severe contamination and marked species losses in receiving streams. However, little is known about how this stress alters food webs and ecosystem function. I conducted a literature review, which revealed that AMD-impacted streams generally had depauperate benthic communities dominated by a few tolerant species and impaired ecosystem processes. Next, using survey and experimental-based approaches, I investigated food web structure and energy flow in these highly stressed streams, which typically have low pH (< 3), high concentrations of dissolved metals (Al, Fe), and substrata coated with metal hydroxide precipitates, on the South Island, New Zealand. Inputs of AMD caused substantial loss of consumers and reduced the overall number of links between species generating small and simplified food webs, with few invertebrates and no fish. Comparative analysis of food webs from a survey of 20 streams with either anthropogenic or natural sources of acidity and metals, indicated that anthropogenic sources had a stronger negative effect on food web properties (size, food chain length, number of links); an effect driven primarily by differences in consumer diversity and diet. However, the presence of fewer trophic levels and reduced trophic diversity (detected using isotopic metrics), were common structural attributes in AMD-impacted webs along a pH gradient, regardless of impact level. Furthermore, complementary dietary analyses of consumer gut contents and stable isotope signatures (δ13C and 15N) confirmed that primary consumers fed generally on basal resources and that there were few predatory interactions, which reflected low densities of small-bodied chironomids. This suggests that food quantity was unlikely to limit primary consumers but that reduced prey availability may be an additional stressor for predators. In these radically re-structured food webs, trophic bottlenecks were generated at the primary consumer level and energy flow to higher consumers was disrupted. However, streams still retained some limited function, including slow leaf litter breakdown, which provided detrital resources and supported the small food webs. Overall, my findings have furthered our understanding of these highly stressed stream ecosystems by providing new insights into interactions among species and trophic levels that structure food webs and enable function.

Acid mine drainage (AMD) is a major environmental issue worldwide. On the West Coast of the South Island, New Zealand, numerous catchments receive AMD, with significant negative impacts on in-stream flora and fauna. Diatoms are commonly regarded as powerful biological indicators and may be found in high abundance in AMD-contaminated streams; however, relatively little work has been done on diatoms in mining environments in New Zealand. Initially, I conducted a survey of epiphytic diatom communities in 39 streams ranging from non-impacted reference streams to those severely impacted by AMD. Streams were assigned to one of four classes along an AMD gradient: circum-neutral reference, naturally acidic reference, moderately impacted, and severely impacted. There was a wide range in diatom taxonomic richness in reference and moderately impacted streams (8 – 33 taxa). Taxonomic richness was greatly reduced in severely impacted streams (1 – 5 taxa) at a threshold of pH 3.4 and was dominated by Pinnularia cf. acidophila (69 – 100% relative abundance). Community composition differed between circum-neutral reference, moderately, and severely impacted streams; however, naturally acidic and moderately impacted streams had similar diatom communities primarily composed of acid-tolerant Eunotia and Frustulia species. This indicated that diatoms are strongly structured by pH and able to tolerate moderate conductivity and metal concentrations without a corresponding shift in community composition. Survey data were then used to develop two diatom-based indices for streams impacted by AMD: a single Biotic Index and a Multimetric Index. While neither index was able to distinguish naturally acidic from moderately impacted streams, both indices successfully categorised streams as circum-neutral reference, moderately or severely impacted by AMD. These indices may be useful in assessing AMD impact on circum-neutral streams or in identifying when a stream has crossed a threshold from moderately to severely impacted by AMD. Diatoms would be especially useful as bioindicators of AMD if they respond rapidly to a change in mine discharge. To test this, mature algal biofilms were reciprocally transferred between circum-neutral reference streams and streams of varying degrees of AMD over a period of 13 days. Diatom mortality increased rapidly in the reciprocal transfer between reference and severely impacted streams. Reference communities resembled the ambient diatom community of severely impacted streams 13 days post-transfer. However, in the reverse transfer, a change in community composition was slow to occur. Diatoms respond faster to an increase in pollution than to pollution amelioration. Overall, results indicated that diatom communities may be a useful tool for monitoring the presence and magnitude of AMD in New Zealand streams.

Thesis (M.Sc. (Hons)) -- University of Western Sydney, 2002. / "Master of Engineering (Honours), 2002, University of Western Sydney - Nepean" Bibliography : leaves 135-141.

Thesis (M. Sc.)--University of Canterbury, 2007. / Typescript (photocopy). "June 2007." Includes bibliographical references (leaves 83-94). Also available via the World Wide Web.

Thesis (Ph. D.)--Carleton University, 2001. / Includes bibliographical references (p. 221-249). Also available in electronic format on the Internet.

Thesis (Ph. D.)--West Virginia University, 2010. / Title from document title page. Document formatted into pages; contains xii, 492 p. : ill. (some col.), maps. Includes abstract. Includes bibliographical references.

Thesis (M.S.)--West Virginia University, 2001. / Title from document title page. Document formatted into pages; contains xiv, 214 p. : ill. (some col.), maps (some col.). Includes abstract. Includes bibliographical references (p. 203-209).

Thesis (MSc)--Stellenbosch University, 2015. / ENGLISH ABSTRACT: The use of toxicity tests to evaluate the quality of streams affected by mixtures such as acid mine drainage (AMD), adds value to assessments whereby site-specific toxicological data may identify toxicants that pose a threat to humans. To successfully evaluate the risk of combined mixtures, an improved understanding of the individual components, their uptake, metabolism, excretion and mode of action is required. This study aimed to identify the extent of AMD toxicity in a dose dependant manner on the MCF-7 cell line. The first study site associated with gold mining was chosen as the Tweelopies Stream situated in the Gauteng province of South Africa. The AMD effluent (un-neutralised) contaminating the Tweelopies Stream had undergone pH-neutralisation using a reactor-bed limestone technology incorporating the use of both calcium carbonate (CaCO3) powder and limestone beds. The second study site, the Kromdraai River, is situated in the eMalahleni region of South Africa where a predominance of coal mining exists. The pH -neutralisation of the AMD (un-neutralised) contaminated Kromdraai River was performed using a caustic soda (NaOH) precipitation technique. This study demonstrated the rapid and effective application of the comet assay as a screening tool for AMD-associated DNA breakages in the human cell line, MCF-7. Moreover, the study analysed parameters of cellular survival, DNA fragmentation and variations in morphologies indicative of cellular death. Collectively, the cyto-genetic aberrations observed in the MCF-7 cells as a result of exposure to gold and coal mining associated AMD, confirms the urgency of incorporating high-throughput screening in ecological toxicity assessment to evaluate cellular damage at genetic levels in low dose exposures where detection might be missed. / AFRIKAANSE OPSOMMING: Die gebruik van toksisiteitstoetse om die gehalte van strome te evalueer wat geraak word deur mengsels soos suur mynwater (SM), gee waarde aan spesifieke toksikologiese data van gifstowwe wat 'n bedreiging vir die mens kan identifiseer. Om die risiko van gekombineerde mengsels en hul individuele komponente beter te begrip en suksesvol evalueer, is hul opname, metabolisme, uitskeiding en modus van aksie nodig. Hierdie studie het gepoog om die omvang van SM-toksisiteit in 'n dosis afhanklike wyse op die MCF-7-sellyn te identifiseer. Die eerste studie-area wat gekies is, hou verband met goudmyn-ontginning, en is die Tweelopiesspruit, geleë in die Gauteng-provinsie van Suid-Afrika. Die SM-uitvloeisel (on-geneutraliseerde) wat die Tweelopiesspruit besoedel, het pH-neutralisasie ondergaan met behulp van die integrasie van 'n reaktor-bed kalksorpsietegnologie wat gebruik maak van beide kalsiumkarbonaat (CaCO3) poeier en kalksteenbeddens. Die tweede studie-area, is die Kromdraairivier geleë in die eMalahleni-streek van Suid-Afrika, waar steenkoolontginning die oorheersende aktiwiteit is. Die pH-neutralisasie van die SM (on-geneutraliseerde) in die geval van die Kromdraairivier word met behulp van 'n bytsoda (NaOH) neerslag tegniek, uitgevoer. Hierdie studie het die komeet-toets getoon as 'n vinnige en doeltreffende toepassing vir SM-geassosieerde DNA-breekskade in die menslike sel lyn, MCF-7. Verder het die studie parameters van sellulêre oorlewing, DNA-fragmentasie en variasies in sel morfologieë wat ‘n aanduiding van sellulêre dood is, ontleed. Gesamentlik dui die resultate daarop dat die sitogenetiese afwykings wat in die MCF-7-selle waargeneem is, as 'n gevolg van blootstelling aan goud- en steenkool-geassosieerde SM is. Die studie het verder die dringendheid van die integrasie van hoë-deurset tegnologieë in ekologiese toksisiteitstoetse in selle wat genetiese skade mag ondergaan, na 'n lae dosis blootstelling waar opsporing dalk gemis word, ondersteun.

Na região sul do Brasil, muito aterros sanitários encontram-se próximos a áreas de mineração de carvão, cujos rejeitos são ricos no mineral pirita (FeS2). Este trabalho teve como objetivo estudar o tratamento de lixiviado de aterro sanitário com coagulantes férricos e ferrosos produzidos a partir da oxidação da pirita em meio aquoso. O lixiviado de aterro sanitário foi coletado no Aterro do Município de Campo Bom no Vale do Rio dos Sinos – RS. Pesquisou-se o efeito da dosagem do coagulante e avaliou-se comparativamente o desempenho com coagulantes comerciais produzidos a partir da dissolução de sucata ferrosa em ácido sulfúrico. Os resultados obtidos demostraram que os coagulantes férricos são eficiente no tratamento por coagulação dos lixiviados em dosagens superiores a 1 g/L. Verificou-se também que os coagulantes ferrosos podem ser aplicados no tratamento do chorume pelo processo Fenton (H2O2/Fe). Foram realizados ensaios considerando diferentes misturas de chorume e DAM, com e sem a adição de H2O2. O efeito de coagulação, em ambos os casos, melhorou as características do efluente em termos de carga orgânica, metais pesados e nutrientes. Porém, quando foi adicionado o H2O2 (Reação de Fenton), o efluente final apresentou melhores resultados em relação a cor, COT (Carbono Orgânico Total), nutrientes e, principalmente, em termos de bactérias do grupo coliforme. Os resultados demonstraram que a drenagem ácida de minas, especialmente as mais concentradas e ricas em Fe+2, podem ser empregadas a baixo custo como fonte de ferro para a Reação de Fenton. Desta maneira, surgem novas tecnologias para o tratamento primário de chorume com o uso de coagulante férricos e ferrosos produzidos a partir da oxidação da pirita presente em rejeitos de carvão. / In southern Brazil, most landfills are close to coal mining areas, whose tailings are rich in the mineral pyrite (FeS2). This work aimed at studying the treatment of landfill leachate with ferrous and ferric coagulants produced from the oxidation of pyrite in aqueous media. The landfill leachate was collected in the landfill of the city of Campo Bom in the region of Vale do Rio dos Sinos – RS, Brazil. The effect of the dosage of coagulant was evaluated and compared performance with commercial coagulants produced from the dissolution of ferrous scrap in sulfuric acid was researched for this paper. The results showed that ferric coagulants are effective in the treatment of leachate by coagulation at dosages greater than 1g / L. It was also found that the ferrous coagulants can be applied in the treatment of leachate by Fenton process (H2O2/Fe). Researches have been performed considering different mixtures of manure and AMD (Acid Mine Drainages), with and without the addition of H2O2. The coagulation effect in both cases, improved the characteristics of the effluent in terms of organic load, heavy metals and nutrients. However, when H2O2 (Fenton reaction) was added, the wastewater showed better results for color, TOC (Total Organic Carbon), nutrients, and especially in terms of coliform bacteria. The results showed that acid mine drainage, especially the most concentrated and rich in Fe +2, can be employed at low cost as a source of iron for the Fenton reaction. Thus, there are new technologies for the primary treatment of manure with the use of ferrous and ferric coagulant produced from the oxidation of pyrite present in coal tailings.