Environmental Noise Assessment Corder Park Pump Station Nelson City Council
Report ref:
220423-108
21 June 2012
Revision 2
Document prepared by: Aurecon New Zealand Limited Level 4 139 Carlton Gore Road Newmarket Auckland 1149 New Zealand T: +64 9 520 6019 F: +64 9 524 7815 E: [email protected] W: aurecongroup.com
Document control
Document ID: Hm120614hm corder park environmental noise assessment V3.docx
Rev No Date Revision details Typist Author Verifier Approver
0 16/11/2011 DRAFT FOR INTERNAL REVIEW HM HM FMP
1 14/06/2012 UPDATED REPORT FOR REVISED SITE LAYOUT HM HM FMP DW
2 21/06/2012 MINOR UPDATE HM HM FMP DW
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Environmental Noise Assessment
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Contents
1. Introduction 1
2. Assessment of site 2
3. Environmental noise criteria 3
4. Schedule of Equipment 4
5. Assessment of environmental noise emissions 7
6. Conclusion 8
Appendix A
Equipment data sheets
Appendix B
Planning maps
Appendix C
Predicted noise contours
Appendix D
Noise monitoring results
Environmental Noise Assessment
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1. Introduction
This report details the environmental noise assessment for the proposed pump station located at Corder Park in Nelson. The site is located adjacent Atawhai Drive/ State Highway 6 in Atawhai, Nelson. An aerial image showing the site location relative to the surrounding properties can be seen in Figure 1 below. Distances are provided to the location of the standby generator which is expected to be the dominant noise source on site.
Figure 1 Aerial photo
An existing pump station is currently located on the site which is to be converted to a storage chamber. The proposed development would include four new pumps located in a dry well of depth 5.3m. A generator is also located on site in a below ground Generator & Control Room. Cross sections of the development can be seen in the Aurecons drawings RC004 RC012.
The development will be predominantly underground with batters to the west, south and east sides.
Site location
Existing exchange building
Nearest resident
Existing pump station
Noise monitoring location
Kindergarten
60 m
30 m
Environmental Noise Assessment
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2. Assessment of site
A site visit was conducted on Tuesday 29 November 2011 to assess the site and install a noise logger to conduct unattended noise measurements.
Noise measurements were taken over a 24 hour period using an ARL 316 Type 1 noise logger. The logger was installed approximately 20 metres from the roadway and 10 metres from the existing pump station on site. The location of the logger can be seen in Figure 2.
Figure 2 Location of noise logger on site
The noise environment on the site is dominated by sporadic high speed traffic on Atawhai Drive (State Highway 6) which is typically constant at all hours. Measurements were carried out in general accordance with the provisions of the relevant New Zealand Standards, NZS 6801:1977 Methods of Measuring Noise and NZS 6801:2008 Acoustics measurement of environmental sound. No rain was recorded over the measurement period, there were significant overcast periods. The logger was calibrated before and after measurements. A summary of the recorded noise logger data is shown below in Table 1. Full logging results can be seen in the Appendix D. It can be seen in the noise monitoring charts that noise levels are reasonably constant throughout the night time period, with only the period around 2.00am showing significantly reduced noise levels. Nose levels measured at the logger location are expected to be generally representative of the noise levels at the nearest residents.
Environmental Noise Assessment
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Table 1 Corder park noise logging results
Corder Park Noise monitoring results 29/11/2011 30/11/2011
L90, 15min dBA Leq,15 min dBA L10, 15 min dBA Lmax, 15 min dBA
Daytime
7.00am to 10.00pm
46 66 70 81
Night time
10.00pm to 7.00am
34 57 53 78
The background (L90) noise levels measured at the monitoring location are considered to be representative of those at the residential and kindergarten receivers. However, as the nearest residence is approximately 80 metres further from the highway than the monitoring location, the Leq and L10 levels are expected to be approximately 14 dBA lower at the residence than the measured results.
Table 2 Predicted noise levels at residence
Predicted noise levels at residence
Leq, 15 min dBA L10, 15 min dBA
Daytime
7.00am to 10.00pm 52 56
Night time
10.00pm to 7.00am 43 39
3. Environmental noise criteria
The site is located in the Nelson City Council area and is subject to the conditions stipulated in the Nelson Resource Management Plan. The applicable planning maps and legends for the site can be seen in Appendix B.
The site is zoned as Open Space Recreation with Coastal Environment and Scheduled Site overlays. The Nelson Resource Management Plan for Open Space Recreation Zones stipulates:
OSr37.1: Noise levels measured at or within the boundary of any site in the residential zone must not exceed:
Day time (7am to 10pm Monday to Friday and 9am to 10pm Saturdays Sundays and Public Holidays)
L10 55 dBA
Other times
L10 45 dBA
Lmax 75 dBA
The site is expected to operate 24 hours a day, seven days per week and should therefore comply with the stricter other times criteria.
It is generally accepted that noise emissions from emergency equipment may exceed the Management Plan levels by 5 dBA.
Environmental Noise Assessment
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4. Schedule of Equipment
The following equipment is proposed on the site, the location of each item can be seen in Figure 3.
Figure 3 Proposed site layout
Figure 4 Proposed site cross section
Environmental Noise Assessment
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Table 3 Schedule of proposed equipment
Item of equipment
Number Location Further information Total sound pressure level, L10 dBA
Pump 2 Underground Pump Room 797l/s, 50 Hz, 200kW,
990rpm 77 @ 5 metres
1
Pump 2 Underground Pump Room 307l/s, 50Hz, 20kW,
735rpm 67 @ 5 metres
1
Generator 1 Underground Generator and Control Room
500 kVA 65 dBA @ 7 metres2
75 dBA @ 7 metres3
Transformer 1 External 500 kVA 41 dBA @ 5 metres4
Notes: 1 Based on the speed and power rating of the pumps and the prediction procedure detailed in Engineering Noise Control, David
A Bies and Colin H Hanson, Fourth Edition, Spoon Press 2009. 2POWERGen Super Silent Canopy Type, details in Appendix A
3 POWERGen Soundproofed Type, details in Appendix A
4 Based on AS/NZS 60076.10:2009 Standard Limit and the power rating of the transformer. Sound Power level of 63 dBA.
Noise emissions from the odour control unit proposed to be located to the north of the new buildings are expected to be insignificant.
Noise spectra for the various items of equipment have been assumed for this assessment based on the prediction methodology in Engineering Noise Control by Bies and Hanson (2009) and test data for comparable units provided by POWERGen. A summary of the maximum noise spectra are shown in Figure 5. All equipment suppliers must ensure that selected equipment does not exceed the specified values.
Figure 5 Equipment sound power levels
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45
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60
65
70
75
80
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90
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100
105
110
32 63 125 250 500 1000 2000 4000 8000
So
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ow
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B
Frequency Hz
Predicted sound power levels for equipment
Generator
Transformer
20kW Pump
200kW Pump
Generator exhaust Super Silent Type
Environmental Noise Assessment
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Based on the equipment data, noise emission calculations are based on a maximum reverberant noise level of 90 dBA L10 in the Generator room (super silent model), and 112 dBA L10 in the pump room.
The pumps are located in a 5.3 metre dry pit. The pit, together with the concrete roof provides significant acoustic shielding. Appropriate acoustic treatment will be provided to the access doors and hatches. Access hatches have been assumed to be minimum 3mm steel. It is understood that no ventilation openings are required for the pump room.
The generator and control room is also to be located underground with a concrete roof. Doors are provided to the north side faade. Appropriate acoustic treatment will be provided to the access doors and ventilation openings in the form of acoustic seals and construction material to adequately control noise emissions. It has been assumed that ventilation inlet and exhaust ducts will be provided, with an area of 1m
2 each. Attenuators will be provided to the ventilation air paths, and the genset will be fitted
with appropriate acoustic exhaust silencers to achieve the environmental noise emission criteria. For the purposes of this assessment, it has been assumed that a 900mm long 50% open area attenuator will be required to both the intake and exhaust ventilation paths. Specification of these attenuators will be conducted in the detailed design stage when ventilation fans have been selected. Specification of the exhaust silencers will be developed with assistance from the generator supplier to ensure noise emissions from the exhausts does not exceed 65dBA at 7 metres.
The generator would be tested periodically during the daytime periods. It is expected that the only night time operation would be during an emergency.
The transformer is located outside, to the south of the proposed new building.
The site will be unoccupied and therefore negligible impact from increased traffic noise is expected.
Environmental Noise Assessment
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5. Assessment of environmental noise emissions
A computational model of the site was developed using the environmental noise emission software SoundPLAN 6.4. The model incorporates noise sources, buildings, surrounding terrain and makes predictions of noise emissions to the surrounding receivers. Predicted noise contours are attached in Appendix C. Predictions of noise emissions have been made in general accordance with NZS6082:2008. As shown in the contours, noise emission levels at the site boundary are predicted to comply with the DP noise limit of 45 dBA L10.
Noise propagation from the site was predicted using the ISO9613-2:1996 model under calm meteorological conditions.
The predicted noise levels from the proposed development at the nearest sensitive receivers are shown below.
Table 4 Predicted noise emission levels
Location Standard Operation L10 dBA
Emergency Operation L10 dBA
District Plan noise limits L10 dBA
Normal operation
Day Night
Kindergarten
Environmental Noise Assessment
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6. Conclusion
An acoustic assessment of the proposed pump station at Corder Park in Nelson has been conducted. The assessment included noise measurements on site and prediction of noise emissions from the proposed equipment.
Noise emissions from the proposed site have been predicted using SoundPLAN 6.4 computational noise prediction software. Acoustic mitigation measures in the form of building construction and ventilation treatment for the Generator Room have been provided in order to reduce noise emissions from the site to within the Nelson City Plan requirements. Provided the suitable noise mitigation measures are incorporated into the design, noise emissions from the development can comply with the Nelson City Plan requirements.
Appendix A Equipment data sheets
heath.millerLine
heath.millerLine
heath.millerText Box0.5 MVA
Appendix B Planning maps
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31
30
ATAW
HAI D
R
ATAWHA
I CRES
WAS
TNEY
TER
DODSON VLY RD
RAINBOW DR
WERNETH ST
NOEL
JONE
S DR
CLOVE
LLY S
T
TUI GLEN RD
JACKSON ST
MARY
BANK
RD
JOLLIE ST
GIPPS ST
WINT
ON P
L
MANA
HTS
TRES
ILLIAN
AVE
GLENBRAE ST
DTR4
DTE1
Oldham
Crk
Nelson Haven
Coastal Marine Area (CMA) Is,Unless Otherwise Zoned,All Areas Below AssumedMHWS (See Legend)
MA
P 4
HE
LP
TIP
: T
he
Leg
end
Slid
es O
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Fro
m T
he
Fro
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able
Nea
r F
ron
t P
age
39
41
40
4
3
5
1:5,000MAP 4
Maps Generated by Nelson City Council's GIS SystemThis Publication is Copyright Reserved by Nelson City Council - Cadastral Information derived from the Crown Records System.
CROWN COPYRIGHT RESERVED - Approved for internal reproduction by Nelson City Council
NELSON RESOURCE MANAGEMENT PLAN
OPERATIVE IN PART (EXCLUDING REGIONAL COASTAL PLAN)1 SEPTEMBER 2004
heath.millerLine
heath.millerText BoxSITE LOCATION
#
#
(((((((
(((((((
(((((((
(((((((
#
#
##
G
!
G
1:5,0001:2,500 1:25,0001:10,000
66kV ETL33kV ETL
220kV ETL110kV ETL
Marine ASCV
Flood Overlay
Launching Ramps
Designation Area
Grampians S.R.O.
Services Overlay
Map Limit Outlines
Heritage Precincts
Inundation Overlay
Road To Be Stopped
Nelson City Boundary
Fault Hazard Overlay
Conservation Overlay
Wakefield Quay Precinct
Land Management Overlay
Potential Quarry Overlay
Tahunanui Slump Core S.R.O.
Port Effects Control OverlayHeritage and Landscape Trees
Tahunanui Slump Fringe S.R.O.
Airport Effects Limit Overlay
Port Nelson Ltd Coastal Permit
Heritage and Landscape Woodland
Airport Effects Control OverlayHeritage Building, Object, Place
Airport Effects Advisory Overlay
Bridge Location - (No Rules Apply)
Public Car Parking Square and Places
Proposed Road (IndicativeAlignment Only)
Riparian Overlay (See App6and Zone Chapters)
Outer Limit of AirportEffects Control Overlay
Outer Limit of AirportEffects Advisory OverlayFloodpath Overlay (Also See Note 1,Flood Path Table)
PLANNING MAPS LEGEND(LEFT HAND MAPS ONLY)NOTE 1: Flood Paths not defined on the Planning Maps are shown in a table in the front page of the PlanningMaps.OVERLAYS OVERLAYSAREAS OF SIGNIFICANT CONSERVATIONVALUE (ASCV)
AIRPORT EFFECTS OVERLAYSSee Map A4.1for Extent of Overlays
NATURAL HAZARD OVERLAYS
SLOPE RISK OVERLAYS (S.R.O.)
FLOOD HAZARD OVERLAYS
PORT EFFECTS OVERLAY
ELECTRICAL TRANSMISSION LINES (ETL)
HERITAGE OVERLAYS
DESIGNATIONS
SYMBOLS
MAP EXTENT SYMBOLS
LEGEND
: LEFT
HAND
MAPS
!"$
28 September 2009 Nelson Resource Management Plan
ATAW
HAI D
R
ATAWHA
I CRES
WAS
TNEY
TER
DODSON VLY RD
RAINBOW DR
WERNETH STNO
EL JO
NES D
R
TUI GLEN RD
JACKSON ST
MARY
BANK
RD
JOLLIE ST
GIPPS ST
CR8
NP37
NP73
Nelson Haven
Coastal Marine Area (CMA) Is,Unless Otherwise Zoned,All Areas Below AssumedMHWS (See Legend)
HE
LP
TIP
: T
he
Leg
end
Slid
es O
ut
Fro
m T
he
Bac
k C
ove
r -
Flo
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Tab
le N
ear
Fro
nt
Pag
eM
AP
4
1:5,000
NELSON RESOURCE MANAGEMENT PLAN
OPERATIVE IN PART (EXCLUDING REGIONAL COASTAL PLAN)1 SEPTEMBER 2004
Maps Generated by Nelson City Council's GIS SystemThis Publication is Copyright Reserved by Nelson City Council - Cadastral Information derived from the Crown Rrecords System.
CROWN COPYRIGHT RESERVED - Approved for internal reproduction by Nelson City Council
MAP 4
39
41
40
42
4
3
576
heath.millerLine
heath.millerText BoxSITE LOCATION
RURAL
1:5,0001:2,500 1:25,0001:10,000
INDUSTRIAL
RESIDENTIAL
Leisure Area
CONSERVATION
Higher Density
INNER CITY-FRINGE
Scheduled Streets
Landscape Overlay
Map Limit Outlines
INNER CITY -CENTRE
View Shaft Overlay
Lower Density Area
SUBURBAN COMMERCIAL
Archaelogical Sites
Nelson City Boundary
OPEN SPACE RECREATION
Archaelogical Overlay
Intense Development Area
Lower Density Area (Stoke)
Coastal Environment Overlay
Lower Density Small Holdings Area
Nayland Road South Industrial Area
Higher Density Small Holdings Area
Public Car Parking Squares and Places
Scheduled Site (SEE Chapter 3and Zone Chapters)
Assumed MHWS and Landward Boundary of the CMA (SEE Note 2)
PLANNING MAPS LEGEND(RIGHT HAND MAPS ONLY)
ZONES OVERLAYS
HERITAGE OVERLAYS
SYMBOLS
NOTE 1: Zones are Represented on Right Hand Facing Sheet Only.NOTE 2: Mean High Water Springs (MHWS) as shown on these Planning Maps are indictative only. Where rulesin this Plan require MHWS to be located, This must be done by survey.
CAPITALS = ZONE
Lower Case = Areas Within Zone
MAP EXTENT SYMBOLS
LE
GE
ND
: R
IGH
T H
AN
D M
AP
S
Bridge Location - (No Rules Apply)
Environmental Noise Assessment
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Appendix C Predicted noise contours
PUMPROOM
WETWELL
GEN.ROOM
LEGEND:PREDICTED NOISE LEVELSLA10 dBA
303540455055606570
CLIENT
NEALE PARK SEWER PUMPING STATIONUPGRADE OPTIONS - CONTRACT No. 3142
DATE
TITLE
REVISION DETAILSDATEREV APPROVED
CHECKED
APPROVED
PROJECTDRAWN DESIGNED
220423.001PROJECT No.
SCALE SIZE
DRAWING No. REV
A3Blenheim New Zealand
89 Seymour Street (PO Box 186)
Telephone: +64 3 520 6060
Email: [email protected]
NEW PUMPSTATION - CORDER PARKPREDICTED NOISE LEVELSEMERGENCY OPERATION APPENDIX C2 A
1:750
INFORMATIONNOT FOR CONSTRUCTIONLK HM
A ISSUED FOR INFORMATION
Cad F
ile: P
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ADD\
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ate: 9
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Kidw
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fs: 22
0423
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S, 22
0423
-xr-2
D-co
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, 220
423-
xr-cp
-imag
e
0
SCALE 1:750
7.5 15 30m
PUMPROOM
WETWELL
GEN.ROOM
LEGEND:PREDICTED NOISE LEVELSLA10 dBA
303540455055606570
CLIENT
NEALE PARK SEWER PUMPING STATIONUPGRADE OPTIONS - CONTRACT No. 3142
DATE
TITLE
REVISION DETAILSDATEREV APPROVED
CHECKED
APPROVED
PROJECTDRAWN DESIGNED
220423.001PROJECT No.
SCALE SIZE
DRAWING No. REV
A3Blenheim New Zealand
89 Seymour Street (PO Box 186)
Telephone: +64 3 520 6060
Email: [email protected]
NEW PUMPSTATION - CORDER PARKPREDICTED NOISE LEVELS
NORMAL OPERATION APPENDIX C1 A
1:750
INFORMATIONNOT FOR CONSTRUCTIONLK HM
A ISSUED FOR INFORMATION
Cad F
ile: P
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ADD\
drgs
\civ\f
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s\220
423-
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ate: 9
/12/20
11 2:
40:14
p.m.
N
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Lindy
Kidw
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Xre
fs: 22
0423
-ADG
_A3H
S, 22
0423
-xr-2
D-co
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, 220
423-
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SCALE 1:750
7.5 15 30m
Environmental Noise Assessment
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Appendix D Noise monitoring results
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100
So
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ress
ure
Le
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BA
Time
Corder Park Pump Station, Atawhai Drive, Atawhai
Tuesday 29/11/2011 Wednesday 30/11/2011
Lmax
L10
Leq
L90
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