The Biological Assessment and Rehabilitation of the World’s Rivers: An Overview

Detalhes bibliográficos
Autor(a) principal: Feio, Maria João
Data de Publicação: 2021
Outros Autores: Hughes, Robert M., Callisto, Marcos, Nichols, Susan J., Odume, Oghenekaro N., Quintella, Bernardo R., Kuemmerlen, Mathias, Aguiar, Francisca C., Almeida, Salomé F. P., Alonso-EguíaLis, Perla, Arimoro, Francis O., Dyer, Fiona J., Harding, Jon S., Jang, Sukhwan, Kaufmann, Philip R., Lee, Samhee, Li, Jianhua, Macedo, Diego R., Mendes, Ana, Mercado-Silva, Norman, Monk, Wendy, Nakamura, Keigo, Ndiritu, George G., Ogden, Ralph, Peat, Michael, Reynoldson, Trefor B., Rios-Touma, Blanca, Segurado, Pedro, Yates, Adam G.
Tipo de documento: Artigo
Idioma: eng
Título da fonte: Repositório Científico de Acesso Aberto de Portugal (Repositórios Cientìficos)
Texto Completo: http://hdl.handle.net/10316/93166
https://doi.org/10.3390/w13030371
Resumo: The biological assessment of rivers i.e., their assessment through use of aquatic assemblages, integrates the effects of multiple-stressors on these systems over time and is essential to evaluate ecosystem condition and establish recovery measures. It has been undertaken in many countries since the 1990s, but not globally. And where national or multi-national monitoring networks have gathered large amounts of data, the poor water body classifications have not necessarily resulted in the rehabilitation of rivers. Thus, here we aimed to identify major gaps in the biological assessment and rehabilitation of rivers worldwide by focusing on the best examples in Asia, Europe, Oceania, and North, Central, and South America. Our study showed that it is not possible so far to draw a world map of the ecological quality of rivers. Biological assessment of rivers and streams is only implemented officially nation-wide and regularly in the European Union, Japan, Republic of Korea, South Africa, and the USA. In Australia, Canada, China, New Zealand, and Singapore it has been implemented officially at the state/province level (in some cases using common protocols) or in major catchments or even only once at the national level to define reference conditions (Australia). In other cases, biological monitoring is driven by a specific problem, impact assessments, water licenses, or the need to rehabilitate a river or a river section (as in Brazil, South Korea, China, Canada, Japan, Australia). In some countries monitoring programs have only been explored by research teams mostly at the catchment or local level (e.g., Brazil, Mexico, Chile, China, India, Malaysia, Thailand, Vietnam) or implemented by citizen science groups (e.g., Southern Africa, Gambia, East Africa, Australia, Brazil, Canada). The existing large-extent assessments show a striking loss of biodiversity in the last 2–3 decades in Japanese and New Zealand rivers (e.g., 42% and 70% of fish species threatened or endangered, respectively). A poor condition (below Good condition) exists in 25% of South Korean rivers, half of the European water bodies, and 44% of USA rivers, while in Australia 30% of the reaches sampled were significantly impaired in 2006. Regarding river rehabilitation, the greatest implementation has occurred in North America, Australia, Northern Europe, Japan, Singapore, and the Republic of Korea. Most rehabilitation measures have been related to improving water quality and river connectivity for fish or the improvement of riparian vegetation. The limited extent of most rehabilitation measures (i.e., not considering the entire catchment) often constrains the improvement of biological condition. Yet, many rehabilitation projects also lack pre-and/or post-monitoring of ecological condition, which prevents assessing the success and shortcomings of the recovery measures. Economic constraints are the most cited limitation for implementing monitoring programs and rehabilitation actions, followed by technical limitations, limited knowledge of the fauna and flora and their life-history traits (especially in Africa, South America and Mexico), and poor awareness by decision-makers. On the other hand, citizen involvement is recognized as key to the success and sustainability of rehabilitation projects. Thus, establishing rehabilitation needs, defining clear goals, tracking progress towards achieving them, and involving local populations and stakeholders are key recommendations for rehabilitation projects (Table 1). Large-extent and long-term monitoring programs are also essential to provide a realistic overview of the condition of rivers worldwide. Soon, the use of DNA biological samples and eDNA to investigate aquatic diversity could contribute to reducing costs and thus increase monitoring efforts and a more complete assessment of biodiversity. Finally, we propose developing transcontinental teams to elaborate and improve technical guidelines for implementing biological monitoring programs and river rehabilitation and establishing common financial and technical frameworks for managing international catchments. We also recommend providing such expert teams through the United Nations Environment Program to aid the extension of biomonitoring, bioassessment, and river rehabilitation knowledge globally.
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spelling The Biological Assessment and Rehabilitation of the World’s Rivers: An OverviewEcological statusFreshwaterBiological elementsRestorationReference conditionsThe biological assessment of rivers i.e., their assessment through use of aquatic assemblages, integrates the effects of multiple-stressors on these systems over time and is essential to evaluate ecosystem condition and establish recovery measures. It has been undertaken in many countries since the 1990s, but not globally. And where national or multi-national monitoring networks have gathered large amounts of data, the poor water body classifications have not necessarily resulted in the rehabilitation of rivers. Thus, here we aimed to identify major gaps in the biological assessment and rehabilitation of rivers worldwide by focusing on the best examples in Asia, Europe, Oceania, and North, Central, and South America. Our study showed that it is not possible so far to draw a world map of the ecological quality of rivers. Biological assessment of rivers and streams is only implemented officially nation-wide and regularly in the European Union, Japan, Republic of Korea, South Africa, and the USA. In Australia, Canada, China, New Zealand, and Singapore it has been implemented officially at the state/province level (in some cases using common protocols) or in major catchments or even only once at the national level to define reference conditions (Australia). In other cases, biological monitoring is driven by a specific problem, impact assessments, water licenses, or the need to rehabilitate a river or a river section (as in Brazil, South Korea, China, Canada, Japan, Australia). In some countries monitoring programs have only been explored by research teams mostly at the catchment or local level (e.g., Brazil, Mexico, Chile, China, India, Malaysia, Thailand, Vietnam) or implemented by citizen science groups (e.g., Southern Africa, Gambia, East Africa, Australia, Brazil, Canada). The existing large-extent assessments show a striking loss of biodiversity in the last 2–3 decades in Japanese and New Zealand rivers (e.g., 42% and 70% of fish species threatened or endangered, respectively). A poor condition (below Good condition) exists in 25% of South Korean rivers, half of the European water bodies, and 44% of USA rivers, while in Australia 30% of the reaches sampled were significantly impaired in 2006. Regarding river rehabilitation, the greatest implementation has occurred in North America, Australia, Northern Europe, Japan, Singapore, and the Republic of Korea. Most rehabilitation measures have been related to improving water quality and river connectivity for fish or the improvement of riparian vegetation. The limited extent of most rehabilitation measures (i.e., not considering the entire catchment) often constrains the improvement of biological condition. Yet, many rehabilitation projects also lack pre-and/or post-monitoring of ecological condition, which prevents assessing the success and shortcomings of the recovery measures. Economic constraints are the most cited limitation for implementing monitoring programs and rehabilitation actions, followed by technical limitations, limited knowledge of the fauna and flora and their life-history traits (especially in Africa, South America and Mexico), and poor awareness by decision-makers. On the other hand, citizen involvement is recognized as key to the success and sustainability of rehabilitation projects. Thus, establishing rehabilitation needs, defining clear goals, tracking progress towards achieving them, and involving local populations and stakeholders are key recommendations for rehabilitation projects (Table 1). Large-extent and long-term monitoring programs are also essential to provide a realistic overview of the condition of rivers worldwide. Soon, the use of DNA biological samples and eDNA to investigate aquatic diversity could contribute to reducing costs and thus increase monitoring efforts and a more complete assessment of biodiversity. Finally, we propose developing transcontinental teams to elaborate and improve technical guidelines for implementing biological monitoring programs and river rehabilitation and establishing common financial and technical frameworks for managing international catchments. We also recommend providing such expert teams through the United Nations Environment Program to aid the extension of biomonitoring, bioassessment, and river rehabilitation knowledge globally.MDPI2021info:eu-repo/semantics/publishedVersioninfo:eu-repo/semantics/articlehttp://hdl.handle.net/10316/93166http://hdl.handle.net/10316/93166https://doi.org/10.3390/w13030371eng2073-4441https://www.mdpi.com/2073-4441/13/3/371Feio, Maria JoãoHughes, Robert M.Callisto, MarcosNichols, Susan J.Odume, Oghenekaro N.Quintella, Bernardo R.Kuemmerlen, MathiasAguiar, Francisca C.Almeida, Salomé F. P.Alonso-EguíaLis, PerlaArimoro, Francis O.Dyer, Fiona J.Harding, Jon S.Jang, SukhwanKaufmann, Philip R.Lee, SamheeLi, JianhuaMacedo, Diego R.Mendes, AnaMercado-Silva, NormanMonk, WendyNakamura, KeigoNdiritu, George G.Ogden, RalphPeat, MichaelReynoldson, Trefor B.Rios-Touma, BlancaSegurado, PedroYates, Adam G.info: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:RCAAP2022-05-25T06:28:59Zoai:estudogeral.uc.pt:10316/93166Portal AgregadorONGhttps://www.rcaap.pt/oai/openaireopendoar:71602024-03-19T21:12:08.604022Repositório 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 The Biological Assessment and Rehabilitation of the World’s Rivers: An Overview
title The Biological Assessment and Rehabilitation of the World’s Rivers: An Overview
spellingShingle The Biological Assessment and Rehabilitation of the World’s Rivers: An Overview
Feio, Maria João
Ecological status
Freshwater
Biological elements
Restoration
Reference conditions
title_short The Biological Assessment and Rehabilitation of the World’s Rivers: An Overview
title_full The Biological Assessment and Rehabilitation of the World’s Rivers: An Overview
title_fullStr The Biological Assessment and Rehabilitation of the World’s Rivers: An Overview
title_full_unstemmed The Biological Assessment and Rehabilitation of the World’s Rivers: An Overview
title_sort The Biological Assessment and Rehabilitation of the World’s Rivers: An Overview
author Feio, Maria João
author_facet Feio, Maria João
Hughes, Robert M.
Callisto, Marcos
Nichols, Susan J.
Odume, Oghenekaro N.
Quintella, Bernardo R.
Kuemmerlen, Mathias
Aguiar, Francisca C.
Almeida, Salomé F. P.
Alonso-EguíaLis, Perla
Arimoro, Francis O.
Dyer, Fiona J.
Harding, Jon S.
Jang, Sukhwan
Kaufmann, Philip R.
Lee, Samhee
Li, Jianhua
Macedo, Diego R.
Mendes, Ana
Mercado-Silva, Norman
Monk, Wendy
Nakamura, Keigo
Ndiritu, George G.
Ogden, Ralph
Peat, Michael
Reynoldson, Trefor B.
Rios-Touma, Blanca
Segurado, Pedro
Yates, Adam G.
author_role author
author2 Hughes, Robert M.
Callisto, Marcos
Nichols, Susan J.
Odume, Oghenekaro N.
Quintella, Bernardo R.
Kuemmerlen, Mathias
Aguiar, Francisca C.
Almeida, Salomé F. P.
Alonso-EguíaLis, Perla
Arimoro, Francis O.
Dyer, Fiona J.
Harding, Jon S.
Jang, Sukhwan
Kaufmann, Philip R.
Lee, Samhee
Li, Jianhua
Macedo, Diego R.
Mendes, Ana
Mercado-Silva, Norman
Monk, Wendy
Nakamura, Keigo
Ndiritu, George G.
Ogden, Ralph
Peat, Michael
Reynoldson, Trefor B.
Rios-Touma, Blanca
Segurado, Pedro
Yates, Adam G.
author2_role author
author
author
author
author
author
author
author
author
author
author
author
author
author
author
author
author
author
author
author
author
author
author
author
author
author
author
author
dc.contributor.author.fl_str_mv Feio, Maria João
Hughes, Robert M.
Callisto, Marcos
Nichols, Susan J.
Odume, Oghenekaro N.
Quintella, Bernardo R.
Kuemmerlen, Mathias
Aguiar, Francisca C.
Almeida, Salomé F. P.
Alonso-EguíaLis, Perla
Arimoro, Francis O.
Dyer, Fiona J.
Harding, Jon S.
Jang, Sukhwan
Kaufmann, Philip R.
Lee, Samhee
Li, Jianhua
Macedo, Diego R.
Mendes, Ana
Mercado-Silva, Norman
Monk, Wendy
Nakamura, Keigo
Ndiritu, George G.
Ogden, Ralph
Peat, Michael
Reynoldson, Trefor B.
Rios-Touma, Blanca
Segurado, Pedro
Yates, Adam G.
dc.subject.por.fl_str_mv Ecological status
Freshwater
Biological elements
Restoration
Reference conditions
topic Ecological status
Freshwater
Biological elements
Restoration
Reference conditions
description The biological assessment of rivers i.e., their assessment through use of aquatic assemblages, integrates the effects of multiple-stressors on these systems over time and is essential to evaluate ecosystem condition and establish recovery measures. It has been undertaken in many countries since the 1990s, but not globally. And where national or multi-national monitoring networks have gathered large amounts of data, the poor water body classifications have not necessarily resulted in the rehabilitation of rivers. Thus, here we aimed to identify major gaps in the biological assessment and rehabilitation of rivers worldwide by focusing on the best examples in Asia, Europe, Oceania, and North, Central, and South America. Our study showed that it is not possible so far to draw a world map of the ecological quality of rivers. Biological assessment of rivers and streams is only implemented officially nation-wide and regularly in the European Union, Japan, Republic of Korea, South Africa, and the USA. In Australia, Canada, China, New Zealand, and Singapore it has been implemented officially at the state/province level (in some cases using common protocols) or in major catchments or even only once at the national level to define reference conditions (Australia). In other cases, biological monitoring is driven by a specific problem, impact assessments, water licenses, or the need to rehabilitate a river or a river section (as in Brazil, South Korea, China, Canada, Japan, Australia). In some countries monitoring programs have only been explored by research teams mostly at the catchment or local level (e.g., Brazil, Mexico, Chile, China, India, Malaysia, Thailand, Vietnam) or implemented by citizen science groups (e.g., Southern Africa, Gambia, East Africa, Australia, Brazil, Canada). The existing large-extent assessments show a striking loss of biodiversity in the last 2–3 decades in Japanese and New Zealand rivers (e.g., 42% and 70% of fish species threatened or endangered, respectively). A poor condition (below Good condition) exists in 25% of South Korean rivers, half of the European water bodies, and 44% of USA rivers, while in Australia 30% of the reaches sampled were significantly impaired in 2006. Regarding river rehabilitation, the greatest implementation has occurred in North America, Australia, Northern Europe, Japan, Singapore, and the Republic of Korea. Most rehabilitation measures have been related to improving water quality and river connectivity for fish or the improvement of riparian vegetation. The limited extent of most rehabilitation measures (i.e., not considering the entire catchment) often constrains the improvement of biological condition. Yet, many rehabilitation projects also lack pre-and/or post-monitoring of ecological condition, which prevents assessing the success and shortcomings of the recovery measures. Economic constraints are the most cited limitation for implementing monitoring programs and rehabilitation actions, followed by technical limitations, limited knowledge of the fauna and flora and their life-history traits (especially in Africa, South America and Mexico), and poor awareness by decision-makers. On the other hand, citizen involvement is recognized as key to the success and sustainability of rehabilitation projects. Thus, establishing rehabilitation needs, defining clear goals, tracking progress towards achieving them, and involving local populations and stakeholders are key recommendations for rehabilitation projects (Table 1). Large-extent and long-term monitoring programs are also essential to provide a realistic overview of the condition of rivers worldwide. Soon, the use of DNA biological samples and eDNA to investigate aquatic diversity could contribute to reducing costs and thus increase monitoring efforts and a more complete assessment of biodiversity. Finally, we propose developing transcontinental teams to elaborate and improve technical guidelines for implementing biological monitoring programs and river rehabilitation and establishing common financial and technical frameworks for managing international catchments. We also recommend providing such expert teams through the United Nations Environment Program to aid the extension of biomonitoring, bioassessment, and river rehabilitation knowledge globally.
publishDate 2021
dc.date.none.fl_str_mv 2021
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dc.identifier.uri.fl_str_mv http://hdl.handle.net/10316/93166
http://hdl.handle.net/10316/93166
https://doi.org/10.3390/w13030371
url http://hdl.handle.net/10316/93166
https://doi.org/10.3390/w13030371
dc.language.iso.fl_str_mv eng
language eng
dc.relation.none.fl_str_mv 2073-4441
https://www.mdpi.com/2073-4441/13/3/371
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