Camilty Wind Farm - Partnerships for Renewables
Camilty Wind Farm - Partnerships for Renewables Camilty Wind Farm - Partnerships for Renewables
Camilty Wind Farm 2.3.14 For some topics where it is very difficult to value an asset and/or quantify the magnitude of the effect (e.g. socio-economics or waste) a simple descriptor – beneficial, neutral or adverse is used to describe the significance of the effect. Table 2.2 Establishing the Level of Effect Importance or Sensitivity of Receptor HIGH MEDIUM LOW NEGLIGIBLE Magnitude of Change LARGE MEDIUM Very substantial or substantial Substantial or moderate SMALL Moderate or slight Slight Substantial or moderate Moderate or slight Negligible Moderate Slight Negligible Slight or negligible Negligible NEGLIGIBLE Negligible Negligible Negligible Negligible Table 2.3 Generic Level of Effect Criteria Level of Effect Very substantial Substantial Moderate Slight Negligible Criteria Only adverse effects are assigned this level of importance as they represent key factors in the decision-making process. These effects are generally, but not exclusively, associated with sites and features of international, national or regional importance that are likely to suffer a most damaging effect and loss of resource integrity. A major change at a regional or district scale site or feature may also enter this category. These beneficial or adverse effects are likely to be very important considerations at a local or district scale and, if adverse, are potential concerns to the scheme and may become material in the decision making process. These beneficial or adverse effects while important at a local scale are not likely to be key decision making issues. Nevertheless, the cumulative effect of such issues may influence decision making if they lead to an increase in the overall adverse effects on a particular area or on a particular resource. These beneficial or adverse effects may be raised as local factors but are unlikely to be of critical importance in the decision making process. Nevertheless they are of relevance in enhancing the subsequent design of the Scheme and consideration of mitigation or compensation measures. No discernible effect within the normal bounds of variation or within the margin of forecasting error. Not normally considered by the decision maker. 2.3.15 While effects are considered to fall into one of five effect categories ranging from ‘negligible’, ‘slight‘, ‘moderate’, ‘substantial’ and ‘very substantial’ in the effects matrix presented in Table 2.2, it is generally only those effects that fall into the ‘moderate’, ‘substantial’ or ‘very substantial’ category that are considered to be the significant environmental effects arising from the construction, operation and decommissioning of the development. It should however be noted that different specialist topics within the ES may use a different approach to identifying which level of effects are significant. March 2013 2-21 ES Chapter 2 The EIA and Scoping Process Copyright Partnerships for Renewables Development Co. Ltd 2013 ©
Camilty Wind Farm 2.3.16 The use of the categories of ‘slight’ or ‘negligible’ is used in acknowledgement that there may be a range of effects and it is also used to assess where, cumulatively, several effects of moderate or less could be deemed to combine to be a substantial or greater effect. Further guidance is contained within paragraph 94 of Circular 3, 2011, The Town and Country Planning (Environmental Impact Assessment)(Scotland) Regulations 2011 which states: “Whilst every ES should provide a full factual description of the development, the emphasis of Schedule 4 is on the ‘main’ or ‘significant’ environmental effects to which a development is likely to give rise. Other impacts may be of little or no significance for the particular development in question and will need only very brief treatment to indicate that their possible relevance has been considered.” 2.3.17 Although the approach to EIA followed in this ES establishes a ‘level’ for all effects identified, from negligible through to very substantial, it should be emphasised that the 2011 EIA Regulations (Schedule 4) only require the likely significant environmental effects to be described. Individual assessment chapters therefore establish on a topic by topic basis which ‘levels of effect’ are deemed to be significant. The summary tables at the end of each assessment chapter therefore clearly state for each effect identified, whether it has been found to be ‘significant’ or ‘not significant’. Type of Effect 2.3.18 The EIA Regulations require consideration of a variety of types of effect, namely direct/indirect, secondary, cumulative, positive/negative, short/medium/long-term, and permanent/temporary. In this ES, effects are considered in terms of how they arise, their valency (i.e. whether they are positive or negative) and duration. Each will have a source originating from the development, a pathway and a receptor. 2.3.19 Predicted effects will be adverse/negative or beneficial/positive; direct or indirect; secondary or cumulative; temporary or permanent; and, short, medium or long term. The nature of each of these effects is defined in Table 2.4, with further discussion relating to cumulative effects provided in the section below. In some cases it is appropriate to identify that the interpretation of a change is a matter of personal opinion, and such effects will be described as ‘subjective’. 2.3.20 The temporal scope of environmental effects is stated where known. Effects are typically described as: • Temporary – these are likely to be related to a particular activity and will cease when the activity finishes. The terms ‘short-term’ and ‘long-term’ may also be used to provide a further indication of how long the effect will be experienced; and • Permanent – this typically means an unrecoverable change. Table 2.4 Types of Environmental Effects Effect Direct Indirect Description Effects arising directly as a result of the construction, operations or decommissioning of the proposed development e.g. removal of ground vegetation to facilitate construction. Effects not caused directly as result of the construction, operations or decommissioning of the proposed development, but arising as a consequence of it. March 2013 2-22 ES Chapter 2 The EIA and Scoping Process Copyright Partnerships for Renewables Development Co. Ltd 2013 ©
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- Page 16 and 17: Camilty Wind Farm 1 Introduction 1.
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<strong>Camilty</strong> <strong>Wind</strong> <strong>Farm</strong><br />
2.3.14 For some topics where it is very difficult to value an asset and/or quantify the magnitude of<br />
the effect (e.g. socio-economics or waste) a simple descriptor – beneficial, neutral or adverse<br />
is used to describe the significance of the effect.<br />
Table 2.2 Establishing the Level of Effect<br />
Importance or Sensitivity of Receptor<br />
HIGH MEDIUM LOW NEGLIGIBLE<br />
Magnitude of Change<br />
LARGE<br />
MEDIUM<br />
Very substantial<br />
or substantial<br />
Substantial or<br />
moderate<br />
SMALL Moderate or slight Slight<br />
Substantial or<br />
moderate<br />
Moderate or<br />
slight<br />
Negligible<br />
Moderate Slight Negligible<br />
Slight or<br />
negligible<br />
Negligible<br />
NEGLIGIBLE Negligible Negligible Negligible Negligible<br />
Table 2.3 Generic Level of Effect Criteria<br />
Level of Effect<br />
Very substantial<br />
Substantial<br />
Moderate<br />
Slight<br />
Negligible<br />
Criteria<br />
Only adverse effects are assigned this level of importance as they represent key<br />
factors in the decision-making process. These effects are generally, but not<br />
exclusively, associated with sites and features of international, national or<br />
regional importance that are likely to suffer a most damaging effect and loss of<br />
resource integrity. A major change at a regional or district scale site or feature<br />
may also enter this category.<br />
These beneficial or adverse effects are likely to be very important considerations<br />
at a local or district scale and, if adverse, are potential concerns to the scheme<br />
and may become material in the decision making process.<br />
These beneficial or adverse effects while important at a local scale are not likely<br />
to be key decision making issues. Nevertheless, the cumulative effect of such<br />
issues may influence decision making if they lead to an increase in the overall<br />
adverse effects on a particular area or on a particular resource.<br />
These beneficial or adverse effects may be raised as local factors but are<br />
unlikely to be of critical importance in the decision making process. Nevertheless<br />
they are of relevance in enhancing the subsequent design of the Scheme and<br />
consideration of mitigation or compensation measures.<br />
No discernible effect within the normal bounds of variation or within the margin of<br />
<strong>for</strong>ecasting error. Not normally considered by the decision maker.<br />
2.3.15 While effects are considered to fall into one of five effect categories ranging from ‘negligible’,<br />
‘slight‘, ‘moderate’, ‘substantial’ and ‘very substantial’ in the effects matrix presented in Table<br />
2.2, it is generally only those effects that fall into the ‘moderate’, ‘substantial’ or ‘very<br />
substantial’ category that are considered to be the significant environmental effects<br />
arising from the construction, operation and decommissioning of the development. It<br />
should however be noted that different specialist topics within the ES may use a different<br />
approach to identifying which level of effects are significant.<br />
March 2013 2-21 ES Chapter 2<br />
The EIA and Scoping Process<br />
Copyright <strong>Partnerships</strong> <strong>for</strong> <strong>Renewables</strong> Development Co. Ltd 2013 ©