Connecting Global Priorities Biodiversity and Human Health
1ZcgwtN
1ZcgwtN
Create successful ePaper yourself
Turn your PDF publications into a flip-book with our unique Google optimized e-Paper software.
een estimated to be 1–2 μg/kg/day, considerably<br />
higher than the WHO recommendation (0.23 μg/<br />
kg/day) (Passos <strong>and</strong> Mergler 2008).<br />
The reduction or elimination of Hg use in<br />
ASGM has been receiving widespread attention<br />
(Veiga 2014). Less damaging options include<br />
amalgamating a gold concentrate rather than the<br />
whole ore <strong>and</strong> using “mercury-free artisanal gold”,<br />
in which gold is isolated by centrifuges <strong>and</strong> the<br />
gangue materials magnetically removed (Drace<br />
et al. 2012). Awareness <strong>and</strong> education about Hg<br />
poisoning in ASGM communities is also essential<br />
to ensuring adherence to such changes in ASGM<br />
technology.<br />
4. Impacts of agriculture on water<br />
ecosystems <strong>and</strong> human health<br />
Unsustainable agricultural practices have<br />
significant impacts on human health, <strong>and</strong> water<br />
pollution from fertilizers, pesticides <strong>and</strong> herbicides<br />
remains a serious problem (see the chapter on<br />
agricultural biodiversity <strong>and</strong> food security in<br />
this volume). Better use of ecosystem services,<br />
underpinned by biodiversity, in agricultural<br />
production systems provides considerable<br />
opportunities to reverse these impacts on health<br />
while simultaneously improving food security.<br />
Agriculture accounts for about 70% of global<br />
water use, <strong>and</strong> physical water scarcity is already a<br />
problem for more than 1.6 billion people (IWMI<br />
2007). It is increasingly recognized that the<br />
management of l<strong>and</strong> <strong>and</strong> water are inextricably<br />
linked (e.g. DEFRA 2004). In Engl<strong>and</strong>, for<br />
example, up to 75% of sediment loading in rivers<br />
can be attributed to agriculture, while 60% of<br />
nitrate pollution <strong>and</strong> 25% of phosphates in surface<br />
waters originates from agriculture (DEFRA 2007).<br />
Agricultural practices can also contribute to the<br />
spread of water-related <strong>and</strong> waterborne disease.<br />
For example, significant E. coli loads have been<br />
found in run-off from l<strong>and</strong> grazed by cattle <strong>and</strong><br />
treated with livestock wastes (Oliver et al. 2005),<br />
all of which impact the quality of water for human<br />
consumption <strong>and</strong> use.<br />
Natural vegetation cover in buffers along rivers is<br />
critical to the regulation of water flow, retention of<br />
nutrients, <strong>and</strong> capture of pollutants <strong>and</strong> sediments<br />
across l<strong>and</strong>scapes (reviewed in Osborne <strong>and</strong><br />
Kovacic 1993). The removal of trees <strong>and</strong> natural<br />
habitats in l<strong>and</strong>scapes affects soil directly, as well<br />
as the quantity <strong>and</strong> quality of water draining<br />
from agricultural systems. Riparian buffers of<br />
non-crop vegetation are widely recommended as<br />
a tool for removing non-point source pollutants,<br />
particularly nutrients (nitrates, phosphorus,<br />
potassium) from agricultural areas, especially<br />
those carried by surface run-off (Lee et al. 2003;<br />
Brüsch <strong>and</strong> Nilsson 1993; Daniel <strong>and</strong> Gilliam<br />
1996; Gl<strong>and</strong>on et al. 1981; Nakamura et al. 2001).<br />
In field studies, even buffers of switchgrass along<br />
fields removed 95% of the sediment, 80% of the<br />
total nitrogen (N), 62% of the nitrate nitrogen<br />
(NO 3 -N), 78% of the total phosphorus (P), <strong>and</strong><br />
58% of the phosphate phosphorus (PO 4 -P). If the<br />
buffer included woody species, it removed 97%<br />
of the sediment, 94% of the total N, 85% of the<br />
NO 3 -N, 91% of the total P, <strong>and</strong> 80% of the PO 4 -P<br />
in the run-off (Lee et al. 2003).<br />
Nutrient run-off from agricultural sources into<br />
waterways has been blamed for the production of<br />
hypoxia, popularly termed (aquatic) “dead zones”<br />
(Diaz 2001). These destroy local fisheries in many<br />
coastal areas, which communities rely on for the<br />
intake of protein <strong>and</strong> other nutrients. Dead zones<br />
have now been reported in more than 400 systems,<br />
affecting a total area of more than 245 000<br />
square kilometres (Diaz <strong>and</strong> Rosenburg 2008;<br />
see Figure 1). These are concentrated along the<br />
eastern seaboard of North America, <strong>and</strong> European<br />
<strong>and</strong> Japanese coastlines, where human ecological<br />
footprints <strong>and</strong> agriculture intensities are highest<br />
(Diaz <strong>and</strong> Rosenburg 2008, see Figure 1).<br />
Agricultural practice <strong>and</strong> its dem<strong>and</strong> for water<br />
have reduced both the amount <strong>and</strong> quality of<br />
drinking water available for human consumption.<br />
At the same time, lack of irrigation in many lowincome<br />
countries is a leading cause of poor crop<br />
production <strong>and</strong> yield gaps (Lobell et al. 2009). By<br />
2002, irrigated agricultural l<strong>and</strong> comprised less<br />
than one fifth of all cropped area but produced<br />
40–45% of the world’s food (Döll <strong>and</strong> Siebert<br />
54 <strong>Connecting</strong> <strong>Global</strong> <strong>Priorities</strong>: <strong>Biodiversity</strong> <strong>and</strong> <strong>Human</strong> <strong>Health</strong>