environmental impact statement kilmainhamwood compost facility ...
environmental impact statement kilmainhamwood compost facility ... environmental impact statement kilmainhamwood compost facility ...
5361- Kilmainhamwood Compost Facility Extension- EIS 10 NOISE AND VIBRATION 10.1 INTRODUCTION This chapter of the EIS shall explore the potential Noise and Vibration impacts associated with the proposed extension to the existing compost facility at Kilmainhamwood, Kells, County Meath. The current application proposes to extend the existing facility buildings in order to provide sufficient processing capacity for the additional tonnage. It is proposed to construct a 38m x 25m extension on the southwest side of the existing facility and an extension 39m x 30m on the northeast side of the existing facility. The proposed extensions to the facility buildings are shown on Drawing No. 5361–2402 and Drawing No. 5361-2403. The extensions to the buildings will a steel portal frame design featuring 3.0m high mass concrete walls and green cladding (to match character of the existing buildings). The height of the proposed extensions will not be any higher than the existing buildings. 10.2 EXISTING ENVIRONMENT The existing environment is already a composting facility which this proposed development seeks to expand. Noise levels for the area are presented below and are taken from the Annual Environmental Reports for the existing facility. Two principal environmental noise parameters were measured which are defined below. LAeq is the A-weighted equivalent continuous steady sound level during the measurement period and effectively represents an average ambient noise value. LA90 is the A-weighted sound level that is exceeded for 90% of the measurement period and is used to quantify background noise level. For inspection purposes only. Consent of copyright owner required for any other use. A-weighting is the process by which noise levels are corrected to account for the non-linearity of human hearing. All noise levels quoted are relative to a sound pressure of 2x10 -5 Pa. Typical ranges of noise levels are presented in Table 10.1 below to compare against the baseline noise levels measured: Table 10.1 Typical Noise Levels in Our Environment Sound levels in decibels dB (A) Description of Activity 0 Absolute silence 25 Very Quiet room 35 Rural night time setting with no wind 55 Day time, busy roadway 0.5km away 70 Busy Restaurant 85 Very busy pub, voice has to be raised to be heard 100 Disco or rock concert 120 Uncomfortably loud, conversation impossible 140 Noise causes pain in ears Source: Guidance Note for Noise in relation to Scheduled activities, 2 nd Edition, EPA 2006. 149 EPA Export 01-06-2010:03:55:59
5361- Kilmainhamwood Compost Facility Extension- EIS A description of the noise monitoring locations is presented in Table 10.2 below. Table 10.2 Noise Monitoring Locations Position No. Description N1 10.2.1 Survey Results At entrance road to existing facility as per Schedule D of waste licence W0195-01 and illustrated on Drawing No. 5361-2406 The Annual Environmental Report noise measurement location was chosen (as per Schedule D of waste licence W0195-01) to represent, as best as practicable, typical noise levels in the surroundings of the facility. A description of these locations and the noise levels measured are detailed below in Figures 10.1 and 10.2. Figure 10.1 Day and night time LAeq values from 2008 and 2009 Annual Environmental Reports dB 65 60 55 50 45 40 35 30 25 19th July 06 21st December 06 13th April 07 30th July 07 Day and night LAeq For inspection purposes only. Consent of copyright owner required for any other use. 29th October 07 Dec-07 Jan-08 Date Apr-08 Day Leq Night Leq The relatively steady state noise levels as shown above from July 2006 through to April 2008, and from February 2009 through to December 2009 would be deemed to be typical of the noise emissions from the site. The elevated reading during the day time in September 2008 was derived from off-site noise sources, including sheep in the adjacent field and a helicopter which was hovering overhead in the area at the time of the survey. This is evident as the work practices were unchanged in this period from those preceding it and following it. This was reported to the EPA as part of the annual environmental report (Appendix 2.4). Sep-08 Feb-09 Jun-09 Sep-09 Dec-09 150 EPA Export 01-06-2010:03:55:59
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5361- Kilmainhamwood Compost Facility Extension- EIS<br />
10 NOISE AND VIBRATION<br />
10.1 INTRODUCTION<br />
This chapter of the EIS shall explore the potential Noise and Vibration <strong>impact</strong>s associated with the<br />
proposed extension to the existing <strong>compost</strong> <strong>facility</strong> at Kilmainhamwood, Kells, County Meath.<br />
The current application proposes to extend the existing <strong>facility</strong> buildings in order to provide sufficient<br />
processing capacity for the additional tonnage. It is proposed to construct a 38m x 25m extension on<br />
the southwest side of the existing <strong>facility</strong> and an extension 39m x 30m on the northeast side of the<br />
existing <strong>facility</strong>. The proposed extensions to the <strong>facility</strong> buildings are shown on Drawing No. 5361–2402<br />
and Drawing No. 5361-2403. The extensions to the buildings will a steel portal frame design featuring<br />
3.0m high mass concrete walls and green cladding (to match character of the existing buildings). The<br />
height of the proposed extensions will not be any higher than the existing buildings.<br />
10.2 EXISTING ENVIRONMENT<br />
The existing environment is already a <strong>compost</strong>ing <strong>facility</strong> which this proposed development seeks to<br />
expand. Noise levels for the area are presented below and are taken from the Annual Environmental<br />
Reports for the existing <strong>facility</strong>.<br />
Two principal <strong>environmental</strong> noise parameters were measured which are defined below.<br />
LAeq is the A-weighted equivalent continuous steady sound level during the measurement period and<br />
effectively represents an average ambient noise value.<br />
LA90 is the A-weighted sound level that is exceeded for 90% of the measurement period and is used<br />
to quantify background noise level.<br />
For inspection purposes only.<br />
Consent of copyright owner required for any other use.<br />
A-weighting is the process by which noise levels are corrected to account for the non-linearity of<br />
human hearing. All noise levels quoted are relative to a sound pressure of 2x10 -5 Pa.<br />
Typical ranges of noise levels are presented in Table 10.1 below to compare against the baseline noise<br />
levels measured:<br />
Table 10.1 Typical Noise Levels in Our Environment<br />
Sound levels in decibels dB (A) Description of Activity<br />
0 Absolute silence<br />
25 Very Quiet room<br />
35 Rural night time setting with no wind<br />
55 Day time, busy roadway 0.5km away<br />
70 Busy Restaurant<br />
85 Very busy pub, voice has to be raised to be heard<br />
100 Disco or rock concert<br />
120 Uncomfortably loud, conversation impossible<br />
140 Noise causes pain in ears<br />
Source: Guidance Note for Noise in relation to Scheduled activities, 2 nd Edition, EPA 2006.<br />
149<br />
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