TY - JOUR
T1 - The biological assessment and rehabilitation of the world’s rivers
T2 - An overview
AU - Feio, Maria João
AU - Hughes, Robert
AU - Callisto, Marcos
AU - Nichols, Susan J.
AU - Odume, Oghenekaro N.
AU - Quintella, Bernardo R.
AU - Kuemmerlen, Mathias
AU - Aguiar, Francisca C.
AU - Almeida, Salomé F. P.
AU - Alonso-EguíaLis, Perla
AU - Arimoro, Francis O.
AU - Dyer, Fiona J.
AU - Harding, Jon S.
AU - Jang, Sukhwan
AU - Kaufmann, Phillip R.
AU - Lee, Samhee
AU - Li, Jianhua
AU - Macedo, Diego R.
AU - Mendes, Ana
AU - Mercado-Silva, Norman
AU - Monk, Wendy
AU - Nakamura, Keigo
AU - Ndiritu, George G.
AU - Ogden, Ralph
AU - Peat, Michael
AU - Reynoldson, Trefor B.
AU - Rios-Touma, Blanca
AU - Segurado, Pedro
AU - Yates, Adam G.
N1 - Funding Information:
The authors acknowledge the support of MJF?Portuguese Foundation of Science and Technology (FCT, I.P.) through MARE strategic project UIDB/04292/2020 and Norma Transit?ria-DL57/2016.; DRM-CNPq (PQ-309763/2020-7), Fapemig (APQ-01432-17) and PRPq/UFMG (ADRC-05/2016); MC-P&D Aneel-Cemig GT-599 and GT-611, and Conselho Nacional de Desenvolvimento Cient?fico e Tecnol?gico No. 304060/2020-8; SFPA-Geobiotec strategic project (UID/GEO/04035/2019), FCT and Department of Biology University of Aveiro; BRT?UDLA project FGE.JMC.19.02; BQ and AM?European Union through Partnership Instrument Grant number PI/2017/388-178?Lot 1?Water Management and Ecological Security and the Ministry of Water Resources of PRC; FCA & PS-Forest Research Centre FCT I.P. (UIDB/00239/2020). FCA is funded by Norma Transit?ria?DL57/2016/CP1382/CT0028 via FCT I.P.
Publisher Copyright:
© 2021 by the authors. Licensee MDPI, Basel, Switzerland.
Copyright:
Copyright 2021 Elsevier B.V., All rights reserved.
Funding Information:
In New Zealand (NZ) regular ecological assessments of freshwaters is required by some laws, primarily the Resource Management Act (1991). There is no national monitoring program, although the National Institute of Water and Atmospheric Research (NIWA) annually monitors the lower reaches of 77 primarily larger rivers throughout the country. As in Australia, freshwater ecological assessments are generally devolved to the regional government. Each of the 16 Regional Councils (or equivalents) are required to conduct regular, usually annual, State of Environment monitoring. The frequency of monitoring, number of sites and parameters measured vary between councils depending on political, economic, social and cultural pressures. Furthermore, some city councils of larger cities (e.g., >50,000) have limited annual monitoring programs. Some other agencies (e.g., Department of Conservation, Fish and Game NZ) have targeted, often species specific, monitoring. Several rehabilitation projects funded by private organizations or individuals may conduct short-term, limited parameter monitoring.
Publisher Copyright:
© 2021 by the authors. Licensee MDPI, Basel, Switzerland.
PY - 2021/2/1
Y1 - 2021/2/1
N2 - 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.
AB - 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.
KW - Biological elements
KW - Ecological status
KW - Freshwater
KW - Reference conditions
KW - Restoration
UR - http://www.scopus.com/inward/record.url?scp=85101072346&partnerID=8YFLogxK
U2 - 10.3390/w13030371
DO - 10.3390/w13030371
M3 - Review article
SN - 0310-0367
VL - 13
SP - 1
EP - 45
JO - Water
JF - Water
IS - 3
M1 - 371
ER -