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in Context the SCotian Shelf - COINAtlantic

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whales, <strong>the</strong> sperm whale and <strong>the</strong> Nor<strong>the</strong>rn bottlenose<br />

whale, was carried out for <strong>the</strong> Scotian <strong>Shelf</strong> <strong>in</strong><br />

light of ongo<strong>in</strong>g petroleum exploration activities <strong>in</strong> <strong>the</strong><br />

area (LGL Llimited and Malme 2000).<br />

4.5 Pollution<br />

Shipp<strong>in</strong>g, petroleum exploration and development,<br />

disposal at sea (e.g., of dredg<strong>in</strong>g material) and fish<strong>in</strong>g<br />

activities all discharge wastes <strong>in</strong>to <strong>the</strong> mar<strong>in</strong>e<br />

environment. However, <strong>the</strong> largest source of mar<strong>in</strong>e<br />

pollution comes from land-based activities, <strong>in</strong>clud<strong>in</strong>g<br />

agricultural runoff, w<strong>in</strong>d-blown debris, <strong>in</strong>dustrial<br />

activity, and municipal waste-water (Environment<br />

Canada 2004). Stewart and White (2001) provide<br />

a general overview of contam<strong>in</strong>ants on <strong>the</strong> Scotian<br />

<strong>Shelf</strong>. Some mar<strong>in</strong>e sources of pollution on <strong>the</strong><br />

Scotian <strong>Shelf</strong> are briefly described here.<br />

The offshore oil and gas <strong>in</strong>dustry discharges treated<br />

water <strong>in</strong>to <strong>the</strong> mar<strong>in</strong>e environment. Oil and<br />

gas operators are expected to meet guidel<strong>in</strong>es<br />

published by <strong>the</strong> CNSOPB (CNSOPB/C-NLOPB<br />

2010). Discharges from <strong>the</strong> shipp<strong>in</strong>g <strong>in</strong>dustry<br />

are regulated; however, <strong>the</strong>re are <strong>in</strong>cidental and<br />

accidental releases of fuel, chemicals, ship debris<br />

and cargoes (Stewart and White 2001) as well as<br />

occasional major events, such as <strong>the</strong> s<strong>in</strong>k<strong>in</strong>g of<br />

<strong>the</strong> oil tanker, Arrow, <strong>in</strong> Chedabucto Bay <strong>in</strong> 1970<br />

(Environment Canada 2010). The major sources<br />

of pollution from <strong>the</strong> fish<strong>in</strong>g <strong>in</strong>dustry are lost or<br />

abandoned fish<strong>in</strong>g gear and garbage. Two studies<br />

carried out <strong>in</strong> <strong>the</strong> 1990s found that fish<strong>in</strong>g<br />

was <strong>the</strong> most important source of mar<strong>in</strong>e litter <strong>in</strong><br />

offshore areas of <strong>the</strong> Scotian <strong>Shelf</strong> (Lucas 1992;<br />

Dufault and Whitehead 1994). S<strong>in</strong>ce <strong>the</strong>n, fishermen’s<br />

organizations have been active <strong>in</strong> develop<strong>in</strong>g<br />

programs to encourage fishermen to br<strong>in</strong>g<br />

garbage back to shore. The federal government<br />

has also developed awareness brochures and<br />

o<strong>the</strong>r awareness tools (DFO 2007b).<br />

4.6 Cumulative Effects<br />

A cumulative effect may be def<strong>in</strong>ed as “a change<br />

to <strong>the</strong> environment caused by an action <strong>in</strong><br />

comb<strong>in</strong>ation with o<strong>the</strong>r past, present and future<br />

human actions” (Hegmann et al. 1999). Cumulative<br />

effects are important when <strong>the</strong> effects of an<br />

ocean use are persistent over time (i.e., difficult<br />

to reverse), such as pollution with heavy metals<br />

and some pesticides or large-scale destruction of<br />

habitat, or when activities are <strong>in</strong> close proximity <strong>in</strong><br />

time and space. When environmental effects of<br />

activities are considered separately, <strong>the</strong>y may all<br />

be below <strong>the</strong> threshold levels that cause impacts.<br />

Some effects, although thought to be transitory<br />

or of m<strong>in</strong>or importance on <strong>the</strong> scale of a s<strong>in</strong>gle<br />

source (e.g., a vessel discharge, an otter trawler,<br />

an oil well, or a seismic survey) may prove to be<br />

of more serious concern when comb<strong>in</strong>ed. Cumulative<br />

effects need to be addressed at vary<strong>in</strong>g<br />

scales, from local/site-specific to broader regional<br />

ecosystems.<br />

4.7 Multiple Use<br />

Some portions of <strong>the</strong> Scotian <strong>Shelf</strong> experience<br />

relatively high or <strong>in</strong>tensive levels of use, such<br />

as heavily fished areas, hydrocarbon production<br />

areas, and high vessel traffic areas. Parts of <strong>the</strong><br />

outer shelf and shelf break, for example, has been<br />

subject to an <strong>in</strong>creas<strong>in</strong>g <strong>in</strong>tensity of multiple use,<br />

<strong>in</strong>clud<strong>in</strong>g oil and gas development and a variety of<br />

fisheries. O<strong>the</strong>r areas rema<strong>in</strong> little to moderately<br />

used. Current and anticipated expansion, however,<br />

of exist<strong>in</strong>g uses (e.g., deep water fisheries) coupled<br />

with <strong>the</strong> potential for new ocean uses, such<br />

as offshore m<strong>in</strong>erals development or w<strong>in</strong>d power<br />

generation, underscores <strong>the</strong> grow<strong>in</strong>g requirement<br />

for effective multiple use management practices.<br />

http://co<strong>in</strong>atlantic.ca/<strong>in</strong>dex.php/state-of-<strong>the</strong>-scotian-shelf<br />

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