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BOC Immingham Dissolved Acetylene Project Environmental Statement: Vol. 2 Main Text<br />

Assessment Step Description<br />

3 Environmental<br />

baseline<br />

A discussion of the existing conditions, services and physical<br />

natural environment of the site and its surroundings. This includes<br />

consideration of sensitivity and importance of the existing<br />

environmental conditions (as appropriate).<br />

4 Potential impacts Identification and evaluation of the proposed Dissolved Acetylene<br />

Project’s potential impacts in quantitative and qualitative terms.<br />

Impacts have been considered in terms of direct or indirect, shortterm,<br />

medium-term or long-term, permanent or temporary,<br />

positive or negative effects.<br />

5 Assessment and<br />

significance of effects<br />

Following the identification of potential impacts (Step 4), the<br />

environmental baseline data (Step 3) have been used to predict<br />

any changes to the existing conditions and to allow an<br />

assessment of these changes.<br />

The assessment of a potential impact takes into account any<br />

methods to reduce the impact that are already incorporated into<br />

the design and assumes that ‘good practice’ will be applied.<br />

For impacts relating to emissions (e.g. noise, stack gases), a<br />

‘source-pathway-receptor’ viii approach has been taken to<br />

determine whether the identified potential impacts could result in<br />

an environmental effect.<br />

The effect that a project may have on each type of environmental<br />

receptor is influenced by the sensitivity of the baseline<br />

environment and the predicted degree of alteration from the<br />

baseline state.<br />

Significance of an impact has been evaluated in terms of the<br />

magnitude of impact and sensitivity of the receptor. For impacts<br />

effects where an assessment of significance cannot be<br />

determined (e.g. for reasons of uncertainty) this issue has been<br />

highlighted and an explanation given as to why this is the case.<br />

Criteria (as identified in Step 2) have been used in the<br />

assessment process to define the significance of effects. Specific<br />

criteria have been defined in each impact assessment chapter but<br />

are generally considered as:<br />

Major: substantial fundamental changes in an ecosystem ix ,<br />

society, or economy. Changes are well outside the range of<br />

natural variation and unassisted recovery could be protracted.<br />

Moderate: a material but non-fundamental change in an<br />

ecosystem, society, or economy. Changes may exceed the range<br />

of natural variation. Recovery could occur in the long-term.<br />

Minor: a detectable but non-material change in an ecosystem,<br />

society or economy. Changes might be noticeable, but fall within<br />

the range of normal variation.<br />

Negligible: changes in an ecosystem, society, or economy that<br />

are unlikely to be noticeable (i.e. well within the scope of natural<br />

variation).<br />

viii The source-pathway-receptor approach typically involves an estimate of the quantity and composition of material which could escape<br />

(source), the routes by which it could travel offsite (pathways) and the environmental sensitivity of the receiving environment (receptors).<br />

For there to be an environmental effect all three linkages must be present. If connecting source-pathway-receptor linkages cannot be<br />

identified then there is no environmental effect and no need to progress further with the environmental assessment.<br />

ix The term ‘ecosystem’ can be taken to mean the physical environment and the biological communities that live within that environment.<br />

Typically impacts to biological populations and communities are considered rather than impacts to individuals.<br />

5100935.404 Environmental Statement August 2011 56

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