02.06.2016 Views

Connecting Global Priorities Biodiversity and Human Health

1ZcgwtN

1ZcgwtN

SHOW MORE
SHOW LESS

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>

Hooray! Your file is uploaded and ready to be published.

Saved successfully!

Ooh no, something went wrong!