Best policy, scientific practice and engineering solutions for mining-polluted river systems
Submitting Institution
Newcastle UniversityUnit of Assessment
Civil and Construction EngineeringSummary Impact Type
EnvironmentalResearch Subject Area(s)
Earth Sciences: Physical Geography and Environmental Geoscience
Environmental Sciences: Environmental Science and Management
Engineering: Environmental Engineering
Summary of the impact
Research into the characteristics and remediation of mining pollution has
had sustained and significant impacts (2008 - 2013) on environmental
policy and practice at regional, national and international scales.
Impacts, all with documentary evidence, include:
- Defining locations for engineering interventions to manage pollution
in the economically important River Tyne and its estuary (S1).
- Triggering, and supporting delivery of, multi-million pound government
investment in remediation of mining pollution nationally (S2, S3, S4).
- Determining design of the first large-scale `passive' metal mine
drainage treatment system ever built in the UK (S3, S5).
- Ensuring European mining pollution issues are properly addressed in
production of definitive international guidelines on mining pollution
management (S6).
- Shaping of public policy and practice for management of water in
mining regions of Peru and Honduras via international advisory roles (S7,
S8).
Underpinning research
Key research insights relating to impact:
Establishing metal sources and flux in mining-polluted catchments
under varying hydrological conditions: A key research
achievement of the Newcastle University (NU) team (previously referred to
as the HERO Group) relates to the sources, significance and fate of metal
contaminants from, and within, mining catchments (2004 - present; G3,
G5, G7). Carefully designed experiments comprising
simultaneous river flow and quality measurements, with equivalent
measurements of polluting discharges, illustrated the importance of
diffuse sources of mining-related pollution and also the substantial metal
fluxes to freshwaters occurring during periods of high flow (e.g. O1).
Impacts are in Section 4(B). More detailed research on metal fluxes in the
River Tyne catchment (G5) revealed the critical role of abandoned
mine pollution in determining metal levels in estuarine sediments, with
implications for estuary dredging operations specifically, and catchment
management more generally (2009 - 2011). Sensitivities surrounding the
economic implications of the findings mean that this research is
commercial-in-confidence. Impacts are in Section 4(A).
Quantifying the scale and impacts of mine water pollution:
The first ever assessment of the scale and impacts of abandoned base metal
mines on freshwater systems of England and Wales was undertaken by the NU
team (2007 - 2009; G3), developing an impact assessment
methodology founded primarily on hydrochemical data and hosted on a GIS (O2).
This was successfully applied across the nation (2009 - 2010) to highlight
key regions affected by mining-related pollution, and continues to be used
by the Environment Agency (EA) (Section 4(B)). Careful interrogation of
the data revealed the very substantial scale of abandoned mining pollution
in England and Wales for the first time: the problem affects 7-8% of all
waters in England and Wales, and it is responsible for at least 50% of all
the metals in our freshwaters (O3).
Developing novel passive treatment systems for metal-polluted
waters: The NU team's development of sustainable (`passive')
mine water treatment systems initially investigated coal mine water
treatment (e.g. G1), but more recently the main contaminants in
abandoned base metal mine drainage have been the focus (O4, G6, G7).
The research focused on enhancing rates of bacterial sulphate reduction in
compost bioreactors in particular, and demonstrated the potential for
successful treatment in much smaller systems than previously thought
possible. Impacts are in Section 4(C).
Policy and management research in catchments impacted by mining:
Starting from experiences in the UK, the NU team worked with the European
Commission services and WWF policy unit at the interface between the Water
Framework Directive (WFD) and Directive on Mining Waste (2001 - 2004; G2),
producing the first published guidelines on management of catchments with
mining (O5), and experiencing first-hand European policy-making. In
2005 - 2010 the group continued this line of research in European projects
(e.g. G4) with groups in Peru, Chile and Bolivia. These projects
also involved the production of general guidelines in Spanish (UNESCO) and
specific policy guidelines for the research catchments (S8). Key
aspects of this research were published in O6. Impacts are in
Section 4(E). Impacts from coupling of policy and technical insights are
in Section 4(D).
Names of key researchers and positions held:
Dr Jaime Amezaga: RA, 1999 - 2002, SRA, 2002 - 2007, Senior Lecturer,
2007 on
Dr Adam Jarvis: Environment Agency Research Fellow, 2004 - 2007; Senior
Lecturer, 2007 - 2013; Reader, 2013 on
Professor Paul Younger: Reader, 1999 - 2001, Professor, 2001 - 2012
Dr Catherine Gandy: RA, 2002 on; Dr Will Mayes: RA, 2003 - 2009; Dr Tobias
Rötting: RA, 2007 - 2010
References to the research
Key outputs (Note: Key publications are O3, O4 and O6):
[O1] Gozzard E, Mayes WM, Potter HAB, Jarvis AP (2011) Seasonal
and spatial variation of diffuse (non-point) source zinc pollution in a
historically metal mined river catchment, UK. Environ. Pollut., 159,
3113-3122.
[O2] Mayes WM, Johnston D, Potter HAB, Jarvis AP (2009) A national
strategy for identification, prioritisation and management of pollution
from abandoned non-coal mine sites in England and Wales. I. Methodology
development and initial results. Sci. Total Environ., 407(21), 5435-5447.
[O3] Mayes WM, Potter HAB, Jarvis AP (2010) Inventory of aquatic
contaminant flux arising from historical metal mining in England and
Wales. Sci. Total Environ., 408, 3576-3583. (Quantifies, for the first
time, impacts and extent of metal mine pollution nationally)
[O4] Mayes WM, Davis J, Silva V, Jarvis AP (2011) Treatment of
zinc-rich acid mine water in low residence time bioreactors incorporating
waste shells and methanol dosing. J. Hazard. Mater., 193, 279-287. (Demonstrates
scientific principles of novel passive treatment prior to scale-up)
[O5] ERMITE Consortium (2004) Mining impacts on freshwater
environments. In: Mine Water Environ., 23 (Supplement 1), S2-S80.
[O6] Amezaga JM, Rötting TS, Younger PL, Nairn RW, Noles A-J,
Oyarzún R, Quintanilla J (2011) A rich vein? Mining and the pursuit of
sustainability. Environ. Sci. Technol., 45, 21-26. (Illustrates
underlying principles of best international environmental policy and
practice)
Key research grants (PI in parentheses):
[G1] EC FP5, 2000-03, PIRAMID: Passive In-situ remediation of
acidic mine/industrial drainage, €1.5M (Younger)
[G2] EC FP5, 2001-04, ERMITE: Environmental Regulation of Mine
waters in the European Union, €1M (Amezaga)
[G3] Defra/Environment Agency, 2007 - 09, Identification and
prioritisation of abandoned non-coal mine pollution (NoCAM), £200K
(Jarvis)
[G4] EC FP6, 2007-10, CAMINAR: Catchment management and Mining
Impacts in Arid and Semi-arid South America), €1.8M (Amezaga).
[G5] Port of Tyne Authority/Environment Agency/Newcastle City
Council/ONE North East/North Tyneside Council, 2009-11, River Tyne
sediment study, £220K (Jarvis)
[G6] EA/Defra, 2009-12, Mitigation of pollution from abandoned
metal mines, £267K (Jarvis)
[G7] Coal Authority, 2012-13, Non-coal mine water pollution
programme, £278K (Jarvis)
Details of the impact
Research into the characteristics and remediation of mining pollution has
had sustained and significant impacts on policy and practice at regional,
national and international scales. Examples of impacts within the period
01/08 - 07/13, all with documentary evidence, include:
(A) Regional impact on the economy and environment
On research undertaken by the Newcastle University team on the River Tyne
the Minister for the North East of England at the time of the impact,
commented that (S1):
"... our hopes for the regeneration of industrial Tyneside, and the
thousands of jobs that already rely on that regeneration, are
underpinned by the work you have undertaken"
This impact arose from applying research findings (e.g. O1) on
metal fluxes under varying hydrological conditions (2010 - 2012), and
demonstrated that metal pollutants in estuarine sediments of the River
Tyne are associated with abandoned mines 60 km upstream, not contemporary
industry located on the banks of the estuary. This has critically shaped
plans for engineering interventions to address the problems (S1).
(B) National impact on policy makers and the environment
NU research (O2, O3) demonstrated that 8% of all
waterbodies in England and Wales fail to meet EU WFD objectives due to
pollution from abandoned mines (S2). This directly informed Defra's
decision to release £10.5M of funding to the EA (S3) in 2011,
specifically to monitor pollution effectively and construct new treatment
systems. NU has had a major impact in both areas of work, as detailed
below. Abandoned metal mines are explicitly mentioned (page 37) in HM
Government's White Paper on water (December 2011) as a result of the NU
team's quantification of the problems, and data from the team's research
is used in the White paper (S4). In allocating these funds to
specific activities the Deputy Chief Scientific Adviser at Defra stated (S3):
"..in utilising £1.2 million of this funding (during 2012 - 2013) the
Environment Agency has directly adopted the monitoring practices
recommended by the Newcastle University team.."
and, in relation to the first large-scale passive mine water treatment
system to be built, that
"funded from Defra's £10.5 million investment, via the Coal Authority,
the treatment process and system size were directly determined by the
Newcastle team ..."
These are clear statements of the impact of the team's research from
2009, in influencing government policy and investment in environmental
problems, on the environment regulator's practices in addressing this form
of pollution, and on the engineering solutions adopted for treating mine
water pollution (more details below).
(C) National impact on practitioners and the environment
The UK Coal Authority (CA) engaged the NU team (2011) to lead on the
design of the first ever large-scale passive metal mine water treatment
system in the UK, a £1M system that commenced construction in September
2013. The Director of Operations at the Coal Authority acknowledges that (S5):
"The overall treatment process, including treatment unit type and
size, was determined by Newcastle University following research and
development by the research team between 2009 and 2012 ..."
This will be the blueprint for schemes in the coming decades (S5).
The treatment system is a directly scaled up version of the
bioreactors developed through research (G6, G7, O4),
thus clearly linking the research and impact.
The EA is undertaking nationwide investigations (from 2012) of
mining-polluted river catchments, at a cost of £1.2M (S3). The
catchments were selected directly from NU research (G3, O2).
The EA has modified its approach to monitoring based on the NU team's
recommendations in light of its research on diffuse pollution (O1,
S3). Recognising the importance of the work, both EA and CA engaged
the NU team to deliver training courses (2010 - 2011) on mining pollution
to 75 of their organisations' staff i.e. virtually all of their staff
involved in mining pollution. The CA has commented on these training
courses that "... no other organisation has provided more technical
training to our staff ... than the Newcastle University team" (S5).
(D) International impact on practitioners
Internationally, the Global Acid Rock Drainage (GARD) Guide was an
initiative of the world's major mining houses. The GARD Guide is the first
comprehensive international guidance document on mining pollution
management. A web-based document (http://www.gardguide.com),
as at 04/2013 the GARD Guide had been accessed by 161,000 users, 176,000
by 06/2013 (S6), 193,000 by 08/2013, and 206,000 by 10/2013. Two
members of the NU team sat on the committees that shaped both the
structure and content of the Guide (2008 - 2009), and so the team is
indirectly having a continuing impact on the practice of thousands of
professionals worldwide.
That NU was the only organisation in the world to be represented twice on
these committees (http://www.inap.com.au/committees.htm)
is recognition by the international mining community of the impact of the
team's applied research, and a reflection of the team's unique
understanding of both technical and policy issues related to mining
pollution in Europe (S6). The multinational mining company Rio
Tinto stated that (S6):
"...there is no question that the Newcastle University team has had a
worldwide impact on the practice of professionals in the mining sector
dealing with mine water pollution"
The clear influence of the NU team is further made plain in Section 1,
Chapter 1 of the GARD Guide: "The target audience is adapted from a
model developed by the PIRAMID Consortium (2003)"; a reference to
the major output, authored by the NU team, of an EC project led by NU (http://www.imwa.info/piramid/files/PIRAMIDGuidelinesv10.pdf;
G1). The GARD Guide also references the team's policy work, such as
G2 (O5).
(E) International impacts on public policy and services
Underpinned by research in Europe and the Americas (G2, G4,
O6), NU's work in the Arequipa region of Peru had impacts on public
policy and services; the team led the formation of an official advisory
group which wrote guidelines on river basin management in mining areas for
the Arequipa region, with involvement from all key stakeholders (S8).
Because of this expertise the NU team has been engaged by the Catholic
Agency for Overseas Development (CAFOD) Andean Programme (2012 - 2013) to
provide policy advice and support to local authorities and civil society
in one of the highest profile mining conflicts in Peru (Tintaya mine,
Espinar), and were officially accepted by the environmental working group
set up by the Prime Minister's Office (S7), with participation of
three Ministries, to resolve these issues (S7). Consequently the
team has had direct impact on the establishment of long-term monitoring
programmes, definition of regional policies overseas, and the practices of
NGOs, as recognised by CAFOD, that comments (S7):
"Working with Newcastle University has opened a series of different
options and strategies for changing government policy and practice which
had previously been closed to NGOs"
Sources to corroborate the impact
[S1] Testimonial from former Minister for the North East of
England
[S2] see http://www.environment-agency.gov.uk/business/topics/pollution/36564.aspx
[S3] Testimonial from Deputy Chief Scientific Adviser, Defra
[S4] HM Government's White Paper on Water (Dec 2011), Figure iv,
page 30, and page 37
(http://www.official-documents.gov.uk/document/cm82/8230/8230.pdf)
[S5] Testimonial from Director of Operations, Coal Authority.
[S6] Testimonial from Global Practice Leader, Energy, Environment
and Climate Change, Rio Tinto
[S7] Testimonial from Head of Latin America & Caribbean,
Catholic Agency for Overseas Development (CAFOD)
[S8] Jiménez P, Amezaga J, Rötting T, Guzmán E (2010) El Río
Chili: Cuenca Árida con presencia minera. Universidad Nacional de San
Agustin. ISBN: 978-612-45662-1-9.