Statistical modeling of surface water quality in the Ave River Basin
Autor(a) principal: | |
---|---|
Data de Publicação: | 2022 |
Idioma: | eng |
Título da fonte: | Repositório Científico de Acesso Aberto de Portugal (Repositórios Cientìficos) |
Texto Completo: | http://hdl.handle.net/10348/11224 |
Resumo: | Water quality is defined as the set of physical, chemical and biological parameters that allow its use for a specific purpose. The civilization evolution is accompanied by the contamination of water resources due to anthropogenic activities. To mitigate and prevent pollution, it is necessary to carry out systematic research to understand the cause-effect interactions and predict the state of water resources. With the implementation of the Water Framework Directive, there has been more research in the scope of water quality to achieve the directive goals. At the moment, 2027 is the target year to reach the good ecological status of all surface waters in Europe. In Portugal, a large part of the surface waters require improvement to fulfil the objective. In this sense, this dissertation was carried out to study the water quality of the Ave River Basin, given its history of pollution, which is still problematic. With an environmental dataset comprising water quality data, point-source pressures, diffuse pressures and landscape metrics, a sequence of statistical studies were performed, with the main objective of understanding which are the most unsettling pressures. It was chosen statistical models rather than physical because in statistical approaches new discoveries can be found, since models are driven by the dataset. It is highlighted that the created models for the Ave River Basin can be applied to any other basin, it is of national interest that the developed studies become reproduced in other basins/hydrographic regions. The first chapter presents a brief introduction about the main sources of contamination on surface water and the approach to this problem. The second chapter presents a study of cause-effect interactions through structural equation models. It demonstrates the dynamics between point pressures, diffuse pressures, diffuse indicators with surface water contamination and effects on ecological integrity in two river basins. The created models for the Ave River Basin showed better results than for Sabor, since the determination coefficient was higher, and the cause-effect relationships were according to theoretical expectation. Thus, the results revealed that point source pressures and livestock production are decreasing Ave River Basin water quality. The third chapter presents an adapted structural equation model for water quality prediction, according to the future scenarios presented in the 2nd cycle of the River Basin Management Plans. This analysis was performed to identify if, even under an environmentally optimistic scenario, the ecological status of surface waters will improve. For that scenario, it is confirmed that the water quality can improve. Still, IPtIN scores will not achieve the highest categories, indicating that the WFD goal of achieving a good or higher ecological status category for European surface waters until 2027 will not be achieved. In the fourth chapter, land-use metrics are approached in order to verify the relationship between landscape and water quality. In multiple structural equation models, contaminant emissions are compared with the effect of land configuration, in an analysis that comprises different sampling scales, also verifying the differences in these relationships between two seasons. By comparing the weights of measured variables and path coefficients of latent variables, it was observed that the adopted scale is important to trace contamination and landscape effects, such as seasons. It was also noted that the sampling scale, entire drainage area, is the scale that resulted in the highest determination coefficients, so it was decided to use that scale for further studies. Upon discovering that the landscape is a determining factor in the water quality of Ave River Basin, the following question arises: has the landscape always affected this river basin, whose water quality is historically impacted by point source pressures? In Chapter 5, this question is answered, demonstrating which landscape metrics have a dominant effect over about 30 hydrological years, as well as the most unsettling metrics regarding landscape changes. It was concluded that landscape has always been related to Ave River Basin water quality and that interventions and strategies to ensure that landscape does not evolve in a tendency that decreases water quality are measures to adopt. As the landscape has always affected the water quality, it remains to apply the landscape metrics in spatial prediction models of water quality parameters. In chapter 6, linear regression and spatially weighted regression models are demonstrated, in which several regressors were tested, including landscape metrics, point source and diffuse pressures. As a by-product of this task, a Python algorithm was developed to find the best linear regressions within a dataset, regarding the statistical assumptions. By applying the algorithm to the case study, it was possible to predict pH (highest performance), nitrates, total alkalinity, and electrical conductivity (worst performance). For other parameters, namely oxygen demands, it was not obtained regressions regarding statistical assumptions. In chapter 7 it is presented a decision support tool, elaborated through two combined multi-criteria analyses, in which sub-basins are prioritized for environmental intervention, regarding the contamination risk and intervention complexity. The prioritization analysis was adequate for the case study, since by crossing the intervention priority with the chemical and ecological status, the sub-catchments with lower quality were the ones with the highest priority. Finally, in chapter 8, the main conclusions and possible future studies are presented. |
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Statistical modeling of surface water quality in the Ave River BasinAve River BasinSurface water qualityWater quality is defined as the set of physical, chemical and biological parameters that allow its use for a specific purpose. The civilization evolution is accompanied by the contamination of water resources due to anthropogenic activities. To mitigate and prevent pollution, it is necessary to carry out systematic research to understand the cause-effect interactions and predict the state of water resources. With the implementation of the Water Framework Directive, there has been more research in the scope of water quality to achieve the directive goals. At the moment, 2027 is the target year to reach the good ecological status of all surface waters in Europe. In Portugal, a large part of the surface waters require improvement to fulfil the objective. In this sense, this dissertation was carried out to study the water quality of the Ave River Basin, given its history of pollution, which is still problematic. With an environmental dataset comprising water quality data, point-source pressures, diffuse pressures and landscape metrics, a sequence of statistical studies were performed, with the main objective of understanding which are the most unsettling pressures. It was chosen statistical models rather than physical because in statistical approaches new discoveries can be found, since models are driven by the dataset. It is highlighted that the created models for the Ave River Basin can be applied to any other basin, it is of national interest that the developed studies become reproduced in other basins/hydrographic regions. The first chapter presents a brief introduction about the main sources of contamination on surface water and the approach to this problem. The second chapter presents a study of cause-effect interactions through structural equation models. It demonstrates the dynamics between point pressures, diffuse pressures, diffuse indicators with surface water contamination and effects on ecological integrity in two river basins. The created models for the Ave River Basin showed better results than for Sabor, since the determination coefficient was higher, and the cause-effect relationships were according to theoretical expectation. Thus, the results revealed that point source pressures and livestock production are decreasing Ave River Basin water quality. The third chapter presents an adapted structural equation model for water quality prediction, according to the future scenarios presented in the 2nd cycle of the River Basin Management Plans. This analysis was performed to identify if, even under an environmentally optimistic scenario, the ecological status of surface waters will improve. For that scenario, it is confirmed that the water quality can improve. Still, IPtIN scores will not achieve the highest categories, indicating that the WFD goal of achieving a good or higher ecological status category for European surface waters until 2027 will not be achieved. In the fourth chapter, land-use metrics are approached in order to verify the relationship between landscape and water quality. In multiple structural equation models, contaminant emissions are compared with the effect of land configuration, in an analysis that comprises different sampling scales, also verifying the differences in these relationships between two seasons. By comparing the weights of measured variables and path coefficients of latent variables, it was observed that the adopted scale is important to trace contamination and landscape effects, such as seasons. It was also noted that the sampling scale, entire drainage area, is the scale that resulted in the highest determination coefficients, so it was decided to use that scale for further studies. Upon discovering that the landscape is a determining factor in the water quality of Ave River Basin, the following question arises: has the landscape always affected this river basin, whose water quality is historically impacted by point source pressures? In Chapter 5, this question is answered, demonstrating which landscape metrics have a dominant effect over about 30 hydrological years, as well as the most unsettling metrics regarding landscape changes. It was concluded that landscape has always been related to Ave River Basin water quality and that interventions and strategies to ensure that landscape does not evolve in a tendency that decreases water quality are measures to adopt. As the landscape has always affected the water quality, it remains to apply the landscape metrics in spatial prediction models of water quality parameters. In chapter 6, linear regression and spatially weighted regression models are demonstrated, in which several regressors were tested, including landscape metrics, point source and diffuse pressures. As a by-product of this task, a Python algorithm was developed to find the best linear regressions within a dataset, regarding the statistical assumptions. By applying the algorithm to the case study, it was possible to predict pH (highest performance), nitrates, total alkalinity, and electrical conductivity (worst performance). For other parameters, namely oxygen demands, it was not obtained regressions regarding statistical assumptions. In chapter 7 it is presented a decision support tool, elaborated through two combined multi-criteria analyses, in which sub-basins are prioritized for environmental intervention, regarding the contamination risk and intervention complexity. The prioritization analysis was adequate for the case study, since by crossing the intervention priority with the chemical and ecological status, the sub-catchments with lower quality were the ones with the highest priority. Finally, in chapter 8, the main conclusions and possible future studies are presented.A qualidade da água é definida como o conjunto de parâmetros físicos, químicos e biológicos que permitem a sua utilização para um determinado fim. A evolução da civilização é acompanhada pela contaminação de recursos hídricos por atividades antropogénicas. Para a mitigação e prevenção dos fenómenos de poluição é necessário que seja realizada investigação sistemática, para compreender as relações causa efeito e prever o estado dos recursos hídricos. Com a implementação da Diretiva Quadro da Água, tem havido mais investigação no âmbito da qualidade da água para que os objetivos da diretiva sejam alcançados. Neste momento, o ano de 2027 é o ano alvo para que se atinja o bom estado ecológico de todas as massas de água superficial da Europa. Em Portugal, uma grande parte das massas de água superficial requerem melhoria para o cumprimento do objetivo. Nesse sentido, realizou-se a presente dissertação, para estudar a qualidade da água da bacia hidrográfica do Rio Ave, face ao seu histórico de poluição que é, ainda nos dias de hoje, problemático. Com recurso a dados de qualidade, pressões pontuais, pressões difusas e métricas paisagísticas realizou-se uma sequência de estudos estatísticos, com o principal objetivo de compreender quais são as pressões mais preocupantes sobre as massas de água superficial do Ave. Optou-se pela modelação estatística ao invés da modelação física, pois é na modelação estatística que se encontram novas descobertas, uma vez que os modelos são guiados pelas relações entre variáveis. Salienta-se que os modelos criados para a bacia do Ave podem ser aplicados a qualquer outra bacia, e é de interesse nacional que os estudos desenvolvidos sejam reproduzidos noutras bacias/regiões hidrográficas. No primeiro capítulo apresenta-se uma breve introdução sobre as principais fontes de contaminação de águas superficiais e abordagem ao problema. No segundo capítulo é apresentado um estudo de relações causa-efeito através de modelos de equações estruturais. Demonstra-se assim a dinâmica entre pressões pontuais, pressões difusas, indicadores difusos com a contaminação de águas superficiais e efeitos na integridade ecológica entre duas bacias hidrográficas. Os modelos construídos para a bacia do Ave apresentaram melhores resultados do que para a bacia do Sabor, sendo que os valores do coeficiente de determinação foram mais altos, e as relações causa efeito estavam concordantes com a espectativa teórica. Assim, os resultados indicaram que as maiores pressões a afetar a qualidade da água da bacia do Ave são as pressões pontuais e a produção de gado. No terceiro capítulo, apresenta-se um modelo de equações estruturais adaptado para a previsão da qualidade, aplicando os cenários prospetivos apresentados no 2º ciclo dos Planos de gestão de Regiões Hidrográficas. Nessa análise pretendeu-se identificar se, mesmo perante um cenário ambientalmente otimista o estado ecológico das massas de água irá melhorar. Para esse cenário, verificou-se que pode haver melhoria, mas os valores do IPtIN não atingem as melhores categorias, demonstrando assim que o objetivo da DQA de atingir o bom ou excelente estado ecológico para as massas de águas superficiais não será alcançado até 2027. No quarto capítulo são abordadas métricas de uso do solo, com o intuito de verificar a relação entre paisagem e qualidade da água. Em diversos modelos de equações estruturais, as emissões de contaminantes são comparadas com o efeito da configuração do uso, numa análise que abrange diferentes escalas de amostragem e duas estações do ano. Ao comparar os pesos das variáveis medidas e coeficientes de caminho das variáveis latentes, verificou-se que a escala é um fator crucial para a deteção do efeito das fontes de contaminação e paisagem, bem como a estação do ano. Verificou-se ainda que a escala de amostragem, área de drenagem inteira, é a escala onde se obteve maiores valores do coeficiente de determinação, e assim, foi decido utilizar essa escala nos estudos seguintes. Ao descobrir que a paisagem é um fator determinante na qualidade da água da bacia do Ave, surge a seguinte questão: será que a paisagem sempre teve efeito nesta bacia, cuja qualidade da água é historicamente afetada por pressões pontuais? No capítulo 5 essa questão é respondida, demonstrando quais são as métricas paisagísticas que têm um efeito dominante ao longo de cerca de 30 anos hidrológicos, bem como as métricas mais preocupantes, tendo em conta a evolução da paisagem. Concluiu-se que a paisagem sempre esteve ligada à qualidade da água da bacia do Ave, e que, intervenções e estratégias prevenção para que a paisagem não evolua numa tendência que diminua a qualidade da água, são medidas a adotar. Como a paisagem sempre afetou a qualidade da água, resta aplicar as métricas paisagísticas em modelos de previsão espacial de parâmetros de qualidade. No capítulo 6 são demonstrados modelos de regressão linear e regressão espacialmente ponderada, em que se testaram diversos regressores, incluindo métricas paisagísticas, pressões pontuais e pressões difusas. Como subproduto desta tarefa, apresenta-se ainda um algoritmo desenvolvido em Python, para encontrar as melhores regressões lineares dentro de um conjunto de dados, respeitando os pressupostos estatísticos. Ao aplicar o algoritmo ao caso de estudo, foi possível realizar previsões para o pH (com melhor performance), nitratos, alcalinidade total e condutividade elétrica (pior performance). Para outros parâmetros, nomeadamente carência de oxigénio, não foi possível obter regressões que respeitassem todos os pressupostos estatísticos. No capítulo 7, apresenta-se uma ferramenta de apoio à decisão, elaborada através de duas análises multicritério combinadas, em que são priorizadas sub-bacias para intervenção ambiental, tendo em consideração o risco de contaminação e complexidade de intervenção. A análise de priorização foi adequada para a bacia, visto que ao cruzar a prioridade de intervenção com o estado químico e ecológico, as sub-bacias com baixa qualidade apresentaram maior prioridade de intervenção. Por fim, no capítulo 8, apresentam-se as principais conclusões e possíveis estudos futuros.2022-05-11T14:46:16Z2022-01-18T00:00:00Z2022-01-18doctoral thesisinfo:eu-repo/semantics/publishedVersionapplication/pdfapplication/pdfapplication/pdfhttp://hdl.handle.net/10348/11224engFernandes, António Carlos Pinheiroinfo:eu-repo/semantics/openAccessreponame:Repositório Científico de Acesso Aberto de Portugal (Repositórios Cientìficos)instname:Agência para a Sociedade do Conhecimento (UMIC) - FCT - Sociedade da Informaçãoinstacron:RCAAP2024-03-24T04:27:33Zoai:repositorio.utad.pt:10348/11224Portal AgregadorONGhttps://www.rcaap.pt/oai/openairemluisa.alvim@gmail.comopendoar:71602024-03-24T04:27:33Repositório Científico de Acesso Aberto de Portugal (Repositórios Cientìficos) - Agência para a Sociedade do Conhecimento (UMIC) - FCT - Sociedade da Informaçãofalse |
dc.title.none.fl_str_mv |
Statistical modeling of surface water quality in the Ave River Basin |
title |
Statistical modeling of surface water quality in the Ave River Basin |
spellingShingle |
Statistical modeling of surface water quality in the Ave River Basin Fernandes, António Carlos Pinheiro Ave River Basin Surface water quality |
title_short |
Statistical modeling of surface water quality in the Ave River Basin |
title_full |
Statistical modeling of surface water quality in the Ave River Basin |
title_fullStr |
Statistical modeling of surface water quality in the Ave River Basin |
title_full_unstemmed |
Statistical modeling of surface water quality in the Ave River Basin |
title_sort |
Statistical modeling of surface water quality in the Ave River Basin |
author |
Fernandes, António Carlos Pinheiro |
author_facet |
Fernandes, António Carlos Pinheiro |
author_role |
author |
dc.contributor.author.fl_str_mv |
Fernandes, António Carlos Pinheiro |
dc.subject.por.fl_str_mv |
Ave River Basin Surface water quality |
topic |
Ave River Basin Surface water quality |
description |
Water quality is defined as the set of physical, chemical and biological parameters that allow its use for a specific purpose. The civilization evolution is accompanied by the contamination of water resources due to anthropogenic activities. To mitigate and prevent pollution, it is necessary to carry out systematic research to understand the cause-effect interactions and predict the state of water resources. With the implementation of the Water Framework Directive, there has been more research in the scope of water quality to achieve the directive goals. At the moment, 2027 is the target year to reach the good ecological status of all surface waters in Europe. In Portugal, a large part of the surface waters require improvement to fulfil the objective. In this sense, this dissertation was carried out to study the water quality of the Ave River Basin, given its history of pollution, which is still problematic. With an environmental dataset comprising water quality data, point-source pressures, diffuse pressures and landscape metrics, a sequence of statistical studies were performed, with the main objective of understanding which are the most unsettling pressures. It was chosen statistical models rather than physical because in statistical approaches new discoveries can be found, since models are driven by the dataset. It is highlighted that the created models for the Ave River Basin can be applied to any other basin, it is of national interest that the developed studies become reproduced in other basins/hydrographic regions. The first chapter presents a brief introduction about the main sources of contamination on surface water and the approach to this problem. The second chapter presents a study of cause-effect interactions through structural equation models. It demonstrates the dynamics between point pressures, diffuse pressures, diffuse indicators with surface water contamination and effects on ecological integrity in two river basins. The created models for the Ave River Basin showed better results than for Sabor, since the determination coefficient was higher, and the cause-effect relationships were according to theoretical expectation. Thus, the results revealed that point source pressures and livestock production are decreasing Ave River Basin water quality. The third chapter presents an adapted structural equation model for water quality prediction, according to the future scenarios presented in the 2nd cycle of the River Basin Management Plans. This analysis was performed to identify if, even under an environmentally optimistic scenario, the ecological status of surface waters will improve. For that scenario, it is confirmed that the water quality can improve. Still, IPtIN scores will not achieve the highest categories, indicating that the WFD goal of achieving a good or higher ecological status category for European surface waters until 2027 will not be achieved. In the fourth chapter, land-use metrics are approached in order to verify the relationship between landscape and water quality. In multiple structural equation models, contaminant emissions are compared with the effect of land configuration, in an analysis that comprises different sampling scales, also verifying the differences in these relationships between two seasons. By comparing the weights of measured variables and path coefficients of latent variables, it was observed that the adopted scale is important to trace contamination and landscape effects, such as seasons. It was also noted that the sampling scale, entire drainage area, is the scale that resulted in the highest determination coefficients, so it was decided to use that scale for further studies. Upon discovering that the landscape is a determining factor in the water quality of Ave River Basin, the following question arises: has the landscape always affected this river basin, whose water quality is historically impacted by point source pressures? In Chapter 5, this question is answered, demonstrating which landscape metrics have a dominant effect over about 30 hydrological years, as well as the most unsettling metrics regarding landscape changes. It was concluded that landscape has always been related to Ave River Basin water quality and that interventions and strategies to ensure that landscape does not evolve in a tendency that decreases water quality are measures to adopt. As the landscape has always affected the water quality, it remains to apply the landscape metrics in spatial prediction models of water quality parameters. In chapter 6, linear regression and spatially weighted regression models are demonstrated, in which several regressors were tested, including landscape metrics, point source and diffuse pressures. As a by-product of this task, a Python algorithm was developed to find the best linear regressions within a dataset, regarding the statistical assumptions. By applying the algorithm to the case study, it was possible to predict pH (highest performance), nitrates, total alkalinity, and electrical conductivity (worst performance). For other parameters, namely oxygen demands, it was not obtained regressions regarding statistical assumptions. In chapter 7 it is presented a decision support tool, elaborated through two combined multi-criteria analyses, in which sub-basins are prioritized for environmental intervention, regarding the contamination risk and intervention complexity. The prioritization analysis was adequate for the case study, since by crossing the intervention priority with the chemical and ecological status, the sub-catchments with lower quality were the ones with the highest priority. Finally, in chapter 8, the main conclusions and possible future studies are presented. |
publishDate |
2022 |
dc.date.none.fl_str_mv |
2022-05-11T14:46:16Z 2022-01-18T00:00:00Z 2022-01-18 |
dc.type.driver.fl_str_mv |
doctoral thesis |
dc.type.status.fl_str_mv |
info:eu-repo/semantics/publishedVersion |
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publishedVersion |
dc.identifier.uri.fl_str_mv |
http://hdl.handle.net/10348/11224 |
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http://hdl.handle.net/10348/11224 |
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eng |
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eng |
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RCAAP |
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RCAAP |
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Repositório Científico de Acesso Aberto de Portugal (Repositórios Cientìficos) |
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Repositório Científico de Acesso Aberto de Portugal (Repositórios Cientìficos) |
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Repositório Científico de Acesso Aberto de Portugal (Repositórios Cientìficos) - Agência para a Sociedade do Conhecimento (UMIC) - FCT - Sociedade da Informação |
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