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monitoring plan for portuguese coastal waters water quality and ecology monae introduction key outputs products project team documents links how do i get a copy of this book? send an email here with your postal address and monae in the subject. introduction portugal has a number of important estuaries, which fall under the category of transitional waters two of these, and parts of the rivers which flow into them, form the northwestern and southeastern borders with spain. portugal has an extensive coastal area, which delimits the country to the west and to the south. the project monitoring plan for water quality and ecology of portuguese transitional and coastal waters, or monae, was financed by the portuguese water institute, inag, and carried out by an interdisciplinary team drawn from marine science and management experts in the e.u., u.s. and south africa. it started on february 9th 2004, and had a duration of one year. this project aims to provide the reader with a blueprint for the development of a successful and economically viable monitoring plan, based on soundly formulated hypotheses and containing appropriate verification instruments. data were drawn from many sources, including the databases built during the coastal typology and reference conditions project ticor . the e.u. water framework directive (wfd directive 2000/60/ec) outlines the requirements for monitoring of surface waters in the european union, within the general framework of river basin management plans. three distinct types of monitoring are stipulated, in order to meet the overall goal of assessing the quality status of european waters. the focus of this book is only on transitional (estuarine) and coastal waters, for which the following monitoring types and objectives are defined in the wfd. key outputs and findings a summary of the key outputs and findings of monae are presented below. data overview data collection in portuguese transitional and coastal waters has been carried out regularly in several thematic areas, including hydromorphology, marine geology, water quality, phytoplankton, shellfish and specific pollutants. most of the data collected by institutions in portugal are stored in internal databases. the availability of historical data is thus compromised by data fragmentation, which stems from the lack of coordination of monitoring activities both at a system (e.g. estuary or lagoon) and at national level. the figure below summarises the currently available historical datasets as well as other less accessible data. there is a large quantity of data for portuguese transitional and coastal waters. however the datasets are concentrated both in time and space, which means that in most cases they are not representative of a comprehensive system survey, due to the nature of the sampling design. in several systems the number of sampling stations, although high, covers only part of the system. this issue must be addressed when designing future monitoring plans, since there is a need to choose representative sampling stations in accordance with the water bodies defined for an effective implementation of the wfd. spatial domain an approach for the division of transitional and coastal waters in portugal into water bodies for management and monitoring purposes was developed in monae. two distinct methodologies were used: for the definition of open coastal water bodies literature results were used, and for transitional and restricted coastal water bodies, a bottom-up data analysis approach was carried out. there are common points to both methodologies, since in both cases natural factors such as salinity or morphology are combined with the human dimension, using the significant pressures and/or key elements of state. the application of these methodologies has resulted in the proposed definition of 60 transitional and coastal water bodies for portugal. monitoring plans definitions and guidelines although the general objective of monitoring specified in the wfd is to verify compliance with water quality objectives, or to establish the reasons for non-compliance so that appropriate measures may be put in place where applicable, a monitoring plan should examine these questions in broader terms, from the standpoint of ecosystem health. monitoring activities that address a broad set of aims use indicators as proxies for these. in the wfd, these indicators must include the appropriate biological quality elements (bqe) and supporting quality elements (sqe), and may include others. indicators may have different levels of aggregation, ranging from, for example, combined indices of eutrophication or benthic quality status to the concentration of a particular parameter such as dissolved oxygen, and may be defined collectively as environmental quality proxies (eqp). in the wfd these correspond to different combinations of bqe and sqe. relevant objectives should be defined for management of transitional and coastal waters, forming a set of goals, which may need to be harmonised in time, space, and within the allowable eqp thresholds. three broad groups of management objectives may be defined: water quality objectives e.g. (i) restore and maintain a productive ecosystem with no adverse effects due to pollution; (ii) minimize health risks associated with contact water uses; (iii) estimate adverse impacts of eutrophication, including hypoxia resulting from human activities; conservation objectives e.g. (i) maintain on a landscape level the natural environment of the watershed; (ii) protect existing habitat categories within the watershed to preserve and improve regional biodiversity; human use objectives e.g. (i) support water-related recreation whilst preserving the economic viability of commercial endeavours; (ii) encourage sustainable lifestyles within the watershed, whereby human uses are balanced with ecosystem protection; (iii) empower citizens in the protection and stewardship of the estuary and its watershed. a number of monitoring plans for coastal systems in the e.u. and u.s. have identified several types of indicators that can be used, which may be applied in a complementary manner to address the issues under consideration. these are typically divided into core and research indicators, and are evaluated in distinct types of monitoring plans. this fits in well with the concepts outlined in the wfd and developed in various guidance documents, i.e. that for surveillance monitoring the full spectrum of bqe/sqe needs to be covered, for operational monitoring the indicators need to be far more targeted, and in the case of investigative monitoring the focus is on the detailed understanding of a specific issue. assessment of monitoring success each monitoring plan must set out a number of objectives, which may be grouped into two different types: the first focuses on the outputs, and is effectively an internal audit - verification would include compliance with the various terms of reference for time, space, parameters, methodology, etc. the second type examines the success in terms of outcomes, i.e. it is the component that informs management action. programme implementation (outputs) - these are verifiable targets which may be related to the monae terms of reference, i.e. are the goals and objectives of the plan being met. this answers programmatic questions such as: (a) is the sampling covering the estuaries/coastal systems specified in the plan? (b) is the strategy defined for a particular system (e.g. sampling according to a salinity gradient, particular vertical profiles or seasonality being followed? (c) are the parameters being measured as required by the wfd? (d) are methodology issues (intercalibration of methods, etc.) being handled as recommended? programme effectiveness, i.e. environmental success (outcomes) -a distinct set of targets, based around specific ecological quality achievements, must answer questions such as: (a) are shellfish/finfish areas increasing/decreasing?

URL analysis for monae.org

http://www.monae.org/documents/g5-final
quality
assurance.pdf
http://www.monae.org/documents/monae
book.pdf
http://www.monae.org/documents/uk
monitoring
gbmain
text
1103.pdf
http://www.monae.org/documents/water
framework
directive.pdf
http://www.monae.org/documents/g5m-final
quality
assurance
for
modelling.pdf
http://www.monae.org/documents/eu_us_sci-init.pdf
http://www.monae.org/documents/oil
monitoring.pdf
http://www.monae.org/documents/wfd
cis2.4
(coast)
guidance
on
tcw.pdf
http://www.monae.org/documents/ecss
msd687.pdf
http://www.monae.org/#links
http://www.monae.org/documents/habitats
92-43.pdf
http://www.monae.org/documents/barnegat
bay
monintoring
plan.pdf
http://www.monae.org/documents/monitoring
epa.pdf
http://www.monae.org/documents/san
francisco
bay.pdf
http://www.monae.org/documents/seaward
limit
new
zealand.pdf

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ADMIN

  HANDLE C6211015-LROR

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ADDRESS

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R. Fernando Pessoa, Lote 17

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