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EIA-REP-325d-12 _BB_ - 201.09.14.pdf - SAHRA

EIA-REP-325d-12 _BB_ - 201.09.14.pdf - SAHRA

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8.1.10 Heritage Resources<br />

Based on what was found during the initial site evaluation and the recommendation of the EAP a Heritage Impact<br />

Assessment was undertaken. The Heritage Resources Act 25 of 1999 states:<br />

“Section 38 (3) of the National Heritage Resources Act, 1999 (Act 25 of 1999) states that subject to the<br />

provisions of subsections (7), (8) and (9), any person who intends to undertake a development categorised as-<br />

(c) any development or other activity which will change the character of a site-<br />

(i) exceeding 5 000 m 2 in extent<br />

must at the very earliest stages of initiating such a development, notify the responsible heritage resources<br />

authority and furnish it with details regarding the location, nature and extent of the proposed development.”<br />

The proposed development area lies to the south of Ermelo (10km). The area has been intensively mined over a<br />

long period of time which would have destroyed any possible heritage sites.<br />

8.1.11 Noise<br />

Existing noise sources on site and the immediate surrounds include:<br />

• Agricultural activities on surrounding land;<br />

• Processing Plant: Transportation of raw materials to site, product from the site and transport of staff to<br />

and from site;<br />

• Blasting as a result of mining operations;<br />

• Mining and mineral processing activities at the mining areas to the south east and north east of the site;<br />

and<br />

• Vehicles serving the existing mines and farming communities.<br />

In terms of Regulation 66 of the Mineral and Petroleum Resources Act (Act 28 of 2002) Regulations GN R527, a<br />

holder of a permit or right in terms of the Act must comply with the provisions of the Mine Health and Safety Act<br />

(Act 29 of 1996); as well as other applicable law regarding noise management and control.<br />

Many aspects of mining operations lead to an increase in noise levels over the ambient environmental levels.<br />

This can be temporarily enhanced or the regional impact increased in any direction under the influence of<br />

specific climatic factors such as wind direction, cloud cover and temperature inversion layers.<br />

The impacts of noise levels can be both physical and physiological at the high end of the spectrum but more<br />

commonly impact on communication or create psychological effects at the lower level of the spectrum.<br />

The highest magnitude noise impacts are commonly the high intensity, short duration noise levels created by<br />

blasting in surface or opencast mines. Blasting should not be carried out under very overcast conditions or low<br />

level cloud cover as this increases the noise and vibration transmission. The impact can be reduced through<br />

selection of explosives, sequencing the blasts, deflection by structures and timing of the blasts to coincide with<br />

<strong>EIA</strong>-<strong>REP</strong>-<strong>325d</strong>-11<br />

October 20<strong>12</strong><br />

90

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