Giuliana Ferrero

Dr. Giuliana Ferrero

IHE Delft, Delft, the Netherlands
orcid

Research Focus & Metrics

Academic Career Length

21Years (2006-Present)

(Calculated once Scilit publication data is synced: current year − year of first publication + 1)

Representative Publications

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1 January 2010 in Desalination
Verified
Journal Article
Closed access
JSJan Sipma
Jan Sipma
BOBegoña Osuna
Begoña Osuna
NCNeus Collado
Neus Collado
Hèctor MonclúsHèctor Monclús
Hèctor Monclús
Giuliana FerreroGiuliana Ferrero
Giuliana Ferrero
IRIgnasi Rodríguez-Roda
Ignasi Rodríguez-Roda

1 June 2010 in Bioresource Technology
Verified
Journal Article
Closed access
Hèctor MonclúsHèctor Monclús
Hèctor Monclús
JSJan Sipma
Jan Sipma
Giuliana FerreroGiuliana Ferrero
Giuliana Ferrero
IRIgnasi Rodríguez-Roda
Ignasi Rodríguez-Roda
Joaquim ComasJoaquim Comas
Joaquim Comas

1 August 2017 in Geoforum
Verified
Journal Article
Open access
MRMaria Rusca
Maria Rusca
ABAkosua Sarpong Boakye-Ansah
Akosua Sarpong Boakye-Ansah
ALAlex Loftus
Alex Loftus
Giuliana FerreroGiuliana Ferrero
Giuliana Ferrero
PZPieter van der Zaag
Pieter van der Zaag
Urban political ecology attempts to unravel and politicize the socio-ecological processes that produce uneven waterscapes. At the core of this analysis are the choreographies of power that influence how much water flows through urban infrastructure as well as where it flows, thereby shaping conditions and quality of access in cities. If these analyses have been prolific in demonstrating uneven distribution of infrastructures and water quantity, the political ecology of water quality remains largely overlooked. In this paper, we argue that there is a clear theoretical and practical need to address questions of quality in relation to water access in the South. We show that conceptual resources for considering differentiated drinking water quality are already present within urban political ecology. We then contend that an interdisciplinary approach, highlighting the interdependencies between politics, power, and physiochemical and microbiological contamination of drinking water, can further our understandings of both uneven distribution of water contamination and the conceptualisation of inequalities in the urban waterscape. We illustrate our argument through the case of water supply in Lilongwe, Malawi. Our political ecology analysis starts from an examination of the physicochemical and microbiological quality of water supplied by the formal water utility across urban spaces in Lilongwe. We then present the topography of water (quality) inequalities in Lilongwe and identify the political processes underlying the production of differentiated water quality within the centralised network. This paper thereby serves as a deepening of urban political ecology as well as a demonstration of how this approach might be taken forward in the analysis of urbanism and water supplies.

1 July 2012 in Water Research
Verified
Journal Article
Closed access
Giuliana FerreroGiuliana Ferrero
Giuliana Ferrero
IRIgnasi Rodríguez-Roda
Ignasi Rodríguez-Roda
Joaquim ComasJoaquim Comas
Joaquim Comas

1 May 2019 in International Journal of Hygiene and Environmental Health
Verified
Journal Article
Open access
Giuliana FerreroGiuliana Ferrero
Giuliana Ferrero
KSKaren Setty
Karen Setty
BRBettina Rickert
Bettina Rickert
SGShannan George
Shannan George
ARAngella Rinehold
Angella Rinehold
JBJamie Bartram
Jamie Bartram
The World Health Organization has recommended Water Safety Plans (WSPs), a holistic risk assessment and risk management approach, for drinking-water suppliers across low-, middle- and high-income countries, since publishing its 2004 Guidelines for Drinking-Water Quality. While rapid WSP adoption has occurred, capacity is still catching up to implementation needs. Many countries and regions lack case examples, legal requirements, and training resources for WSPs, corresponding to widespread capacity shortfall in the water supply sector. We undertook a comprehensive review of the literature on capacity building and training for WSPs, with the goal of providing recommendations for multiple stakeholder groups at the scales of individual utilities, national governments, and intermediate units of governance. We propose a WSP training taxonomy and discuss it in relation to the stages of learning (introduction, practice, and reinforcement); describe the importance of customizing training to the target group, local language and circumstances; highlight the relevance of auditing for evaluating change over time; and call for robust methods to monitor WSP capacity development.

11 April 2016 in Environmental Science and Pollution Research
Verified
Journal Article
Closed access
PDF file
YEYuli Ekowati
Yuli Ekowati
GBGianluigi Buttiglieri
Gianluigi Buttiglieri
Giuliana FerreroGiuliana Ferrero
Giuliana Ferrero
JVJennifer Valle-Sistac
Jennifer Valle-Sistac
Silvia Diaz-CruzSilvia Diaz-Cruz
Silvia Diaz-Cruz
IRIgnasi Rodríguez-Roda
Ignasi Rodríguez-Roda