19 research outputs found
Detection, toxicology, environmental fate and risk assessment of nanoparticles in the aquatic environment (DeTER)
Nanotechnology is an emerging technology that
has the potential to impact on all aspects of life and
the economy and is expected to form the basis of
several technological innovations and advances
in the 21st century. The European Commission
defines a nanomaterial as “a natural, incidental
or manufactured material containing particles, in
an unbound state or as an aggregate or as an
agglomerate and where, for 50% or more of the
particles in the number size distribution, one or
more external dimensions is in the size range
1 nm–100 nm”. The production of and demand for
products containing nanomaterials has increased
significantly in recent years. The Nanodatabase
developed by the Technical University of Denmark is a
“living” inventory of commercially available products in
the European consumer market that claim to contain
engineered nanomaterials (ENMs) and currently lists
3037 products. Nanomaterials have a wide range
of potential applications, from everyday uses (such
as improvements in fabrics, paints, cosmetics and
packaging) to medical applications, water and soil
remediation and renewable energy production.
Nanomaterials include both nanoparticles and nanosynthesised
materials. Nanomaterials can be naturally
occurring, inadvertently generated or engineered.
ENMs are intentionally produced and exhibit unique
electrical, magnetic, optical, antimicrobial and
other properties. Silver nanoparticles (AgNPs) are
among the ENMs most often incorporated in nanofunctionalised
consumer products. AgNPs have
been incorporated into a diverse range of consumer
products including plastics, soaps, pastes, metals
and fabrics and have applications in water and soil
remediation. In the Nanodatabase, currently 539 of the
3037 products listed contain silver. Although advances
in nanotechnology and the continued development
of novel ENMs are expected to lead to significant
societal benefits, there is increasing concern that the
unique properties of ENMs may result in potential
hazards for both humans and the environment. ENMs
can be released into various environmental matrices
during their production, use and disposal. ENMs pose
a potential risk to human health through ingestion,
inhalation and contact.
To date, the concentrations of AgNPs in the
aquatic environment have primarily been estimated
through modelling, with predicted environmental
concentrations in the ng/l range. This is largely
because of a dearth of appropriate detection
methods. The aims of this 3-year research project
were to (1) develop and implement methods for
the detection of AgNPs in water; (2) determine the
toxicological properties and environmental fate of
AgNPs in the aquatic environment and (3) develop risk
assessment protocols that can be used to evaluate
the environmental fate of and likely risk from AgNPs in
aquatic pathways.
The suitability of activated charcoal as a capture
material for AgNPs from water was examined.
Samples of 100 μg/l of AgNPs were initially generated
and exposed to activated charcoal for 24 hours to
examine the ability of charcoal to capture AgNPs. The
decrease in silver concentration was measured using
an inductively coupled plasma mass spectrometer.
Following initial investigations, the surface area of the
charcoal was increased, first, with a pestle and mortar
and, second, by milling. The increased surface area of
the milled charcoal increased the capture of the AgNPs
from 11.9% to 63.6%. A hydrochloric acid leaching
procedure was developed that successfully removed
the captured silver, allowing the fraction captured by
the charcoal to be quantified, with an average recovery
rate of 94.8%. The results show that milled activated
charcoal can successfully capture AgNPs from water
samples. Activated charcoal therefore represents a
cost-effective material for the remediation of waters
impacted by AgNPs or other nano-wastes.
A multi-trophic test battery that included three
trophic levels was adopted to assess the ecotoxicity
of AgNPs and silver nitrate (AgNO3) to the algae
Pseudokirchneriella subcapitata, the crustacean
Daphnia spp. and the cnidarian Hydra attenuata.
The standard medium (Jaworski’s medium) and
an ethylenediaminetetraacetic acid (EDTA)-free
medium (Chu#10) were tested concurrently. An
approximately 10-fold improvement in test sensitivity
using EDTA-free medium was observed overall. No
significant difference between the toxicity of AgNP and
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Detection, Toxicology, Environmental Fate and Risk Assessment of Nanoparticles in the Aquatic Environment (DeTER)
the toxicity of AgNO3 was observed. Both Daphnia
pulex and Daphnia magna were compared using
AgNO3 and AgNPs. Daphnia pulex, with a 24-hour
half-maximal inhibitory concentration (IC50) of 9.3 μg/l,
was less sensitive to AgNO3 than Daphnia magna,
with an IC50 of 1.22 μg/l. When tested with AgNPs,
both species yielded similar results, with an IC50 of
7.85 μg/l for Daphnia magna and 4.2 μg/l for Daphnia
pulex. As these IC50 values were substantially higher
than the predicted environmental concentrations,
sub-lethal end points were investigated. Fecundity
was assessed in Daphnia magna, with the number
of offspring reduced by 50% after 14 days and 75%
after 28 days when cultured in 100 ng/l of AgNPs. This
demonstrates that the effects of AgNPs may be seen
at close to environmentally relevant concentrations
on population numbers rather than single individual
organisms. Assessment of the ecotoxicity of AgNPs
using Hydra attenuata gross morphology as the
end point yielded a 96-hour half-maximal effective
concentration (EC50) of 29 μg/l for AgNPs. The effect of
silver on the regeneration of Hydra attenuata was the
most environmentally relevant bioassay investigated
as it is very sensitive and robust and Hydra attenuata
represents benthic dwellers likely to be exposed to
higher concentrations of AgNPs.
The risk assessment involved a number of interlinking
stages. Stage 1 included a review of the state of the
art regarding natural attenuation processes that affect
ENPs in the natural aquatic environment and a review
of current risk assessment strategies. In stage 2 a
suite of laboratory-scale studies were conducted to
better characterise the aggregation potential of AgNPs.
The behavioural indications derived from stages 1
and 2 were used to develop an aquatic risk model
(stage 3), which was used to characterise the likely
residual levels of AgNPs in surface waters. Estimated
initial values indicated a mean AgNP concentration of
4.34 × 10–2 μg/l and this was assumed as a worst-case
scenario for surface water concentrations in Ireland
and used as an initial input value in the risk model.
Seasonal factors were incorporated in the risk model
to account for potential fluctuations in organic matter
and ionic strength, which have been identified as key
influencers of particle stability and eventual fate in
natural water systems. The predicted results from the
model developed indicate that citrate-coated particles
underwent greater removal than polyvinylpyrrolidone
(PVP)-coated AgNPs in both stream water and lake
water, with predicted removal rates after 7 days of
≈70% (stream water) and ≈67% (lake water) for
citrate-coated particles and ≈45% (stream water) and
≈50% (lake water) for PVP-coated AgNPs. Predicted
aquatic concentrations of AgNPs were compared
with toxicity data from project partners to establish if
a risk is posed by current estimated concentrations
of AgNPs in natural waters. The EC50 values from
primary producer (algae) to primary consumer
(Daphnia pulex) to secondary consumer (Hydra
attenuata) exposed to PVP-coated AgNPs were
compared with persistent concentrations of AgNPs
in freshwater systems. The concentrations of AgNPs
used in the model were at levels deemed unlikely to
have toxicity concerns to aquatic organisms (mean
levels in water of 4.34 × 10–2 μg/l). Therefore, at current
predicted water concentrations, AgNPs are unlikely
to present a toxic concern to the aquatic food chain.
Stages 4 and 5 used information generated to assess
potential human exposure through drinking water.
The model incorporated estimated removal rates
for the differing treatment processes. Risk to human
health was calculated based on water consumption
and potential exposure to residual AgNPs using
the hazard quotient (HQ). The HQ is a ratio of the
possible exposure to a particular substance and the
level at which it is expected that no adverse effects
will occur. If the calculated HQ is less than 1 then it is
expected that no adverse health effects will result from
exposure. The predicted HQ indicated that there was
no existing risk through the consumption of drinking
water (HQ of 3.24 × 10–7 for males and 3.84 × 10–7 for
females). However, the increased industrial usage of
nanomaterials in many sectors, in conjunction with the
persistence of AgNPs during drinking water treatment,
suggests the need to constantly monitor levels and
re-assess exposure through drinking water into the
future.ye
Virtue Ethics: A Pluralistic View, by Christine Swanton. Oxford: Oxford University Press, 2003. Pp. 312. ISBN 0-199253889.
Nietzsche on the Function and Creation of Value Systems
ABSTRACT
In this article I reconstruct Nietzsche's largely implicit understanding of how value systems are created. At the heart of this process are affects, which Nietzsche sees as drive-based evaluative feelings. Affects create value systems when they form rational patterns of feeling around the aims of their underlying drives. But Nietzsche sets this process of value creation in a functionalist context in which values work to promote underlying drives through the direct privileging of their aims over the aims of other drives, through encouraging the pursuit of objects and conditions that facilitate the drive's discharge, and through the justification of the affects that create the values in the first place. I show how Nietzsche's functionalism can be reconciled with his commitment to the idea that affects create values. And I test my claims against Nietzsche's analysis of slave morality to show that his interpretations of the morality of custom, asceticism, and noble morality follow the same pattern.</jats:p
Nietzsche, the Anthropologists, and the Genealogy of Trauma
In this paper, I bring the Second and Third Essays of On the Genealogy of Morality into conversation with the anthropological work that Nietzsche uses to inform his understanding of human prehistory. More specifically, I show the ways in which Nietzsche’s genealogical use of prehistory both calls upon and departs from the work of figures like Edward Tylor, John Lubbock, and Albert Hermann Post. This departure is most significant in Nietzsche’s rejection of the progressive or developmental account of social and moral history for an account that emphasizes the way in which morality develops out of the psychological effects of recurring human traumas.</jats:p
Ascetic Slaves: Rereading Nietzsche's <i>On the Genealogy of Morals</i>
ABSTRACT
Most Nietzsche scholars read the third essay of On the Genealogy of Morals as an account of the development of Christian asceticism after the slave revolution in morals. In this article, I argue that that is a misreading of Nietzsche's argument, the consequence of which is a failure to understand Nietzsche's treatment of the transition from noble morality to slave morality. I contend that we can track this transition only once we understand the role of the ascetic priest in the slave revolution. The third essay's account of asceticism, then, is indispensable in understanding how slave morality grows out of priestly values. With this argument in place I begin to trace the deep lines of asceticism in the slave revolt as described in the first essay.</jats:p
<i>The Rise of Politics and Morality in Nietzsche's</i> Genealogy: <i>From Chaos to Conscience</i>
Nietzsche, the Anthropologists, and the Genealogy of Trauma
In this paper, I bring the Second and Third Essays of On the Genealogy of Morality into conversation with the anthropological work that Nietzsche uses to inform his understanding of human prehistory. More specifically, I show the ways in which Nietzsche’s genealogical use of prehistory both calls upon and departs from the work of figures like Edward Tylor, John Lubbock, and Albert Hermann Post. This departure is most significant in Nietzsche’s rejection of the progressive or developmental account of social and moral history for an account that emphasizes the way in which morality develops out of the psychological effects of recurring human traumas
