CONESTOGA MEAT PACKERS LIMITED BRESLAU, ONTARIO

Transcription

CONESTOGA MEAT PACKERS LIMITED
BRESLAU, ONTARIO
ACOUSTIC ASSESSMENT REPORT
Submitted to:
Conestoga Meat Packers Ltd.
313 Menno Street
Breslau, Ontario
N0B 1M0
Prepared by:
AMEC Environment & Infrastructure,
a Division of AMEC Americas Limited
160 Traders Blvd., Suite 110
Mississauga, Ontario
L4Z 3K7
January 2014
TR1213003
Acoustics Assessment Report
313 Menno Street, Breslau, Ontario
January 2014
EXECUTIVE SUMMARY
Conestoga Meat Packers Ltd. (CMP) retained AMEC Environment & Infrastructure, a Division of
AMEC Americas Limited (AMEC) to prepare an application for an Environmental Compliance
Approval (Air & Noise) (ECA) for its hog slaughtering facility located at 313 Menno Street in
Breslau, Ontario. This Acoustic Assessment Report has been prepared as a supplement to the
ECA application for the facility located in Breslau, Ontario (the facility). This detailed acoustic
assessment (site wide) has been completed as the actual separation distance between the
closest receptor and the facility is less than the minimum separation distance required by the
Ministry of Environment (MOE) Noise Screening Process for Section 9 Applications (PIBS
4871e).
Operations at the site include hog receiving, processing, storage, shipping and wastewater
treatment. The existing facility is getting expanded by adding new sources such as, cooling
towers.
Seven representative Points of Reception (PORs), including four vacant lot receptors, are
identified in the vicinity of the site and 13 types of significant noise sources have been identified
and considered for this assessment. These sources include 15 condensing units, two boiler
exhausts, one blower louver, two sludge tanks, one air intake louver, three compressor louvers,
two truck routes, one truck unloading hogs, hogs noise, nine refrigeration trailers, one barn fan
wall, two make up air units and an emergency generator.
The facility is located in a Class 2 area as defined in Publication NPC-300 as the site is located
in a sub-urban area, where the background level is typically caused by urban hum and traffic
noise during daytime hours, but has a low ambient sound level, normally occurring between
19:00 and 23:00 hours. The facility currently operates 5 days a week, 8 hours per day, and is
planning to operate 7 days a week, 24 hours per day. MOE’s exclusionary sound level limits
are used as the criteria for this assessment.
As there are no significant sources of vibration at the site, a vibration assessment is not required
for this facility.
Sound levels for the existing noise sources were obtained through on-site measurements
conducted by AMEC on October 10 and December 06, 2013 and that for the cooling towers
were obtained from the manufacturer data sheets. Receptor noise impact associated with the
operation of the facility was assessed through predictive acoustic modelling. The sound levels
at the receptor reported as part of this acoustic assessment represent the worst-case impact
assuming all significant sound sources are operating simultaneously during daytime, evening
and night time hours. The non-emergency operation (i.e., testing and maintenance) of the
emergency generator is assessed separately as required by the NPC-300 guidelines and a
criterion of 55 dBA is used for the assessment as the generator is tested during daytime hours.
TR1213003
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January 2014
It is expected that the site-attributable noise at all existing residential dwellings (PORs 1, 4 and
6) and vacant lot PORs 2 and 3 during regular facility operations are expected to meet the
applicable guideline limits for the worst-case operation. The predicted sound levels during
emergency generator testing are also expected to meet the applicable guideline limits at all
existing residential dwellings and vacant lot PORs 2, 3 and 7. However, the predicted sound
levels at the vacant lot PORs 5 and 7 are expected to exceed the applicable criteria during
regular facility operations and that at vacant lot POR 5 is expected to exceed the criteria limit
during emergency generator testing. It should be noted that the vacant lands surrounding the
facility are agricultural zoned lands and these vacant lots are considered in this assessment as
they can accommodate a residential dwelling in future. If a residential dwelling is built in the
vacant lots (POR 5 and/or POR 7) the facility will update the acoustic assessment by including
the actual location of the dwelling and a Noise Abatement Action Plan (NAAP) will be prepared
if necessary. Therefore, the facility can be in compliance with the applicable MOE NPC-300
guidelines for daytime, evening and night-time operations for the existing points of reception.
No additional mitigation or a NAAP is required until a residential dwelling is built in vacant lots
receptors (POR 5 or POR 7) considered in this assessment.
TR1213003
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January 2014
TABLE OF CONTENTS
PAGE
EXECUTIVE SUMMARY ......................................................................................................................... ES-I
1.0
INTRODUCTION.............................................................................................................................. 1
2.0
FACILITY DESCRIPTION ............................................................................................................... 1
3.0
NOISE SOURCE SUMMARY .......................................................................................................... 2
4.0
EXISTING MITIGATION MEASURES SUMMARY ......................................................................... 3
5.0
POINT OF RECEPTION SUMMARY .............................................................................................. 3
6.0
APPLICABLE NOISE GUIDELINES ............................................................................................... 4
7.0
IMPACT ASSESSMENT.................................................................................................................. 5
8.0
CONCLUSIONS ............................................................................................................................... 6
9.0
LIMITATIONS AND QUALIFICATIONS.......................................................................................... 7
10.0
REFERENCES................................................................................................................................. 8
LIST OF FIGURES
Figure 1:
Figure 2:
Figure 3:
Figure 4:
Site Aerial Map with Points of Reception Location ..................................................................... 10
Significant Noise Source Location .............................................................................................. 11
Noise Contours for Worst-Case Facility Operation ..................................................................... 12
Noise Contours for Emergency Generator Testing .................................................................... 13
LIST OF TABLES
Table 1: Noise Source Summary ............................................................................................................... 15
Table 2: Point of Reception Noise Impact.................................................................................................. 17
Table 3: Acoustic Assessment Summary Table ........................................................................................ 19
LIST OF APPENDICES
Appendix A:
Appendix B:
Appendix C:
Appendix D:
Appendix E:
Appendix F:
Acoustic Assessment Check List
Land-use Zoning Map
Facility Drawings
Noises Calculations and Measurement Details
Insignificant Noise Sources
Key Parameter Used in the Assessment and Sample Calculations
TR1213003
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January 2014
1.0
INTRODUCTION
Conestoga Meat Packers Ltd. (CMP) retained AMEC Environment & Infrastructure, a Division
of AMEC Americas Limited (AMEC) to prepare a site wide Environmental Compliance Approval
(Air & Noise) (ECA) application for its facility located at 313 Menno Street, Breslau, Ontario.
This Acoustic Assessment Report has been prepared as a supplement to the ECA application
for the facility located in Breslau, Ontario (the facility). This detailed acoustic assessment (site
wide) has been completed as the actual separation distance between the closest receptor and
the facility is less than the minimum separation distance required by the Ministry of Environment
(MOE) Noise Screening Process for Section 9 Applications (PIBS 4871e).
Operations at the site include hog receiving, processing, storage, shipping and wastewater
treatment. The existing facility is getting expanded by adding new sources such as, cooling
towers and the new sources are included in this assessment.
This report provides a complete acoustic assessment, and is intended to meet the requirements
outlined in the following MOE documents:
•
•
NPC-233, “Information to be Submitted for Approval of Stationary Sources of Sound”,
dated October 1995; and
Ontario Ministry of the Environment (MOE), “Guide for Applying for Approval (Air &
Noise) s.9 EPA”, February 2005.
A completed copy of the applicable “Acoustic Assessment Report Checklist”, as provided in the
Guide, has been included in Appendix A.
A detailed vibration impact assessment is not required for this site as there are no significant
sources of vibration at the site (e.g., stamping presses). Therefore, this assessment
concentrates on potential noise impacts only.
An Emissions Summary and Dispersion Modelling Report (ESDM report) for the facility has
been completed by AMEC as part of the ECA amendment application. Where possible, we
have used the same source names and identification numbers as in the ESDM report.
2.0
FACILITY DESCRIPTION
The CMP meat processing facility is used to slaughter and process pork products. Live hogs
are transported by truck to the facility daily and held in pens (barn) prior to slaughtering. Hogs
are guided to a stunning operation, cleaned, de-haired, eviscerated and sent to coolers for
further processing. The cold carcasses are subsequently sent through a series of cutting
operations, with the end product packaged and shipped for resale. The existing operation is
getting expanded by adding new sources such as, cooling towers.
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January 2014
The North American Industry Classification System (NAICS) code for the facility is 311611
described as “Animal (except poultry) Slaughtering”. The site is surrounded by agricultural
zoned land.
The following figure and appendices contain information on facility and points of reception
location and surrounding the facility:
Figure 1:
Appendix B:
Appendix C:
Aerial Map of the Site with Points of Reception Location
Land-use Zoning Map of the Site and Surrounding Area
Facility Drawings
The facility currently operates 5 days a week, 8 hours per day, and is planning to operate 7 days
a week, 24 hours per day.
3.0
NOISE SOURCE SUMMARY
Thirteen (13) types of significant noise sources were identified as being significant (i.e., as
emitting noise at a level where their cumulative noise impacts could be of concern). Where
possible, the same identifiers have been used in the Noise Source Summary Table as in the
ESDM Report.
All significant noise sources identified in the assessment are listed below and their locations are
shown in Figure 2:
•
•
•
•
•
•
•
•
•
•
•
•
•
•
fifteen (15) roof top condensing units;
two roof top boiler exhausts;
one air intake louver;
three compressor louver
two truck routes;
nine refrigeration trailers;
one truck unloading hogs;
one hogs noise;
one barn fan wall;
two make up air units for the barn;
one blower louver for wastewater treatment;
two sludge tanks;
three cooling towers; and
one emergency generator.
Sound Power Levels (PWL) for the existing noise sources were calculated from the measured
sound pressure levels and that for the cooling towers and emergency generator were obtained
from the manufacturers’ data sheets.
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January 2014
A noise source summary is provided in Table 1, including sound power levels, characteristics,
and any applicable noise control measures. Sound power calculations are provided in
Appendix D.
Sound levels from unloading activity reefer trailers were included in the assessment. Truck
movement sound levels were distributed along the transportation routes within the property line.
Under MOE NPC-104 noise guidelines, additional penalties apply to sound sources with
annoying natures, including tonal sounds, quasi-impulsive sounds, and beating sounds (sounds
with cyclically varying amplitudes). Conservatively, a 5 dB penalty was added to sources with
tonal characteristics, as per MOE Publication NPC-104.
All insignificant sources are listed in Appendix E.
Details of noise sources can be found in the following table, figure and appendices:
Table 1:
Figure 2:
Appendix D:
Appendix E:
Noise Source Summary
Significant Noise Source Locations
Noise Calculations
List of Insignificant Noise Sources
a week, 24 hours per day. The facility noise impacts at the sensitive receptors were modeled
for the worst-case operation. To model the worst-case operation, all noise sources, except the
emergency generator, were assumed to operate continuously and simultaneously. The nonemergency operation (i.e., testing and maintenance) of the emergency generator is assessed
separately as required by the NPC-300 guidelines.
4.0
EXISTING MITIGATION MEASURES SUMMARY
There is no noise mitigation proposed or considered in the assessment for the facility noise
sources.
5.0
POINT OF RECEPTION SUMMARY
Noise sensitive points of reception (PORs) of interest under NPC-300 guidelines include the
following noise sensitive land uses:
•
•
•
•
Permanent, seasonal, or rental residences;
Hotels, motels and campgrounds;
Schools, universities, libraries and daycare centres;
Hospitals and clinics, nursing/retirement homes; and
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January 2014
•
Churches and places of worship.
Noise impacts at seven worst-impacted noise sensitive receptors have been considered and
modeled for this assessment. These receptor locations are considered to be representative of
worst-case noise impacts in the area. A description of each receptor is listed below and
summarized in Table 3.
•
•
•
•
•
•
•
Point of Reception 1 – POR1 is a two-storey residential dwelling located approximately
200 m south of the facility.
Point of Reception 2 – POR2 is a vacant Lot located approximately 160 m south of the
facility.
Point of Reception 3 – POR3 is a vacant Lot located approximately 170 m south-east of the
facility.
400 m north-east of the facility.
Point of Reception 5 – POR5 is a vacant lot approximately 50 m north side of the
facility.
690 m north-west of the facility.
Point of Reception 7 – POR7 is a vacant Lot located approximately 50 m west side of
the facility.
The receptor location for the houses is chosen at the highest level window pane (i.e., 4.5 m for
two-story house). The receptor location for the vacant lots (i.e., POR2, POR3, POR5 and
POR7) is chosen at 4.5 m height at the worst impacted location. For the existing houses, the
receptor locations at 1.5 m above ground at 30 m away from the dwelling facade and at 4.5 m
height on the dwelling facade were considered. The receptors presented in this report are the
worst-impacted receptor location only.
The vacant lots surrounding the facility are agricultural zoned lands and these vacant lots are
considered in this assessment as they can accommodate a residential dwelling in future. The
location of the modeled receptors with respect to the site location is also shown in Figure 1.
6.0
APPLICABLE NOISE GUIDELINES
The applicable guidelines used for the CMP facility are the Ministry of the Environment (MOE)
"Stationary Source" guidelines for Class 2 areas, set out in Publication NPC-300 as the site is
located in a sub urban area. The guidelines also stipulate that the assessment consider the
potential noise impact during a predictable worse case hour of operation, which is defined as a
situation when the normally busy activity of the sources coincides with an hour low background
sound.
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January 2014
NPC-300 states that non-impulsive (steady) one hour sound levels (Leq (1hr) from stationary
noise sources in Class 2 areas shall not exceed that of the background, where the background
(typically caused by urban hum) is considered to be:
•
•
•
The higher of 50 dBA or background noise, during daytime hours (0700 - 1900h);
The higher of 45 dBA, or background noise, during the early evening (1900 - 2300h),
and
The higher of 45 dBA, or background noise, during night-time (2300 - 0700h).
In the absence of an ambient sound measurement, MOE’s exclusionary criteria limits are used
for this assessment.
A copy of NPC-300 document can be found at the MOE’s website at www.ene.gov.on.ca.
7.0
IMPACT ASSESSMENT
Noise source sound levels obtained through on-site measurements conducted by AMEC, were
used as inputs to model outdoor noise propagation from the facility to the identified closest
PORs. Off-site sound exposures from CMP operations along with truck movements were
modelled using Cadna/A, a computerized version of the ISO 9613 environmental noise
propagation algorithms, produced by Datakustik GmbH. The modelling took into account the
following factors:
•
•
•
•
•
•
Source sound power level;
Distance attenuation;
Source-receptor geometry including heights and elevations;
Barrier effects of the building and surrounding topography;
Ground and air (atmospheric) attenuation; and
Meteorological effects on noise propagation.
a week, 24 hours per day.
The assessment of predictable worst-case facility impacts was completed through modeling.
The combined Leq (1 hour) dBA values for worst-case were predicted at points of reception
POR 1 to POR 7 using the sound emissions from the individual significant sources. Point of
reception impact summary is provided in Table 2. Noise levels in dBA are predicted at the
modelled receptors for the worst-case operating scenario (without generator operation) and the
noise contours generated are shown graphically in Figure 3. The predicted sound levels at the
modelled receptors for the emergency generator testing are completed separately as per NPC300 and the noise contours generated are shown graphically in Figure 4. Key parameters
included in the model and sample calculations are provided in Appendix F.
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January 2014
The predicted sound levels at the receptors reported as part of this acoustic assessment
represent the worst-case impact assuming all significant sound sources are operating
simultaneously at full capacity. Therefore, it is expected that the maximum noise impact at
reported PORs is provided by this assessment.
Acoustic assessment summary is provided in Table 3. Predicted sound levels at all existing
residential dwellings (PORs 1, 4 and 6) and vacant lot PORs 2 and 3 during regular facility
operations are expected to meet the applicable guideline limits. The predicted sound levels
during emergency generator testing are also expected to meet the applicable guideline limits at
all existing residential dwellings and vacant lot PORs 2, 3 and 7. However, the predicted sound
levels at the vacant lot PORs 5 and 7 are expected to exceed the applicable criteria during
regular facility operations and that at vacant lot POR 5 is expected to exceed the criteria limit
during emergency generator testing. It should be noted that the vacant lands surrounding the
facility are agricultural zoned lands and these vacant lots are considered in this assessment as
they can accommodate a residential dwelling in future. If a residential dwelling is built in the
vacant lots (POR 5 and/or POR 7) the facility will update the acoustic assessment by including
the actual location of the dwelling and a Noise Abatement Action Plan (NAAP) will be prepared
if necessary. Therefore, the facility can be in compliance with the applicable MOE NPC-300
guidelines for daytime, evening and night-time operations for the existing points of reception.
No additional mitigation or a NAAP is required until a residential dwelling is built in vacant lots
receptors (POR 5 or POR 7) considered in this assessment.
The sound pressure levels at the points of reception reported as part of this acoustic
assessment represent the worst-case impact from the facility.
8.0
CONCLUSIONS
An acoustic assessment report has been completed for the CMP facility located at 313 Menno
Street in Breslau, Ontario. The assessment results indicate that predicted sound levels at all
existing residential dwellings (PORs 1, 4 and 6) and vacant lot PORs 2 and 3 during regular
facility operations are expected to meet the applicable guideline limits. The predicted sound
levels during emergency generator testing are also expected to meet the applicable guideline
limits at all existing residential dwellings and vacant lot PORs 2, 3 and 7. However, the
predicted sound levels at the vacant lot PORs 5 and 7 are expected to exceed the applicable
criteria during regular facility operations and that at vacant lot POR 5 is expected to exceed the
criteria limit during emergency generator testing. It should be noted that the vacant lands
surrounding the facility are agricultural zoned lands and these vacant lots are considered in this
assessment as they can accommodate a residential dwelling in future. If a residential dwelling
is built in the vacant lots (POR 5 and/or POR 7) the facility will update the acoustic assessment
by including the actual location of the dwelling and a Noise Abatement Action Plan (NAAP) will
be prepared if necessary. Therefore, the facility can be in compliance with the applicable MOE
NPC-300 guidelines for daytime, evening and night-time operations for the existing points of
reception. No additional mitigation or a NAAP is required until a residential dwelling is built in
vacant lots receptors (POR 5 or POR 7) considered in this assessment.
TR1213003
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January 2014
9.0
LIMITATIONS AND QUALIFICATIONS
This report was prepared exclusively for Lake Erie Concrete Supply Ltd. for specific application
addressed herein. The quality of information, conclusions and estimates contained herein is
consistent with the level of effort involved in AMEC’s services and based on: i) information
available at the time of preparation, ii) data supplied by outside sources, and iii) the
assumptions, conditions and qualifications set forth in the report. This report is intended to be
used by Lake Erie Concrete Supply Ltd. only, subject to the terms and conditions of its contract
with AMEC. Any other use of, or reliance on, this report by a third party other than those
expressly noted in this report is at that party’s sole risk. This report has been prepared in
accordance with generally accepted engineering practice. No other warranty, expressed or
implied, is made.
AMEC Environmental & Infrastructure
a Division of AMEC Americas Limited
Prepared by:
Reviewed by:
Rachel Hackett, B.A.
Environmental Specialist
Mohammed Salim P.Eng.
Senior Acoustics Engineer
Checked by:
Alireza Seifzadeh, M.Sc
Acoustical Specialist
TR1213003
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January 2014
10.0
REFERENCES
Environmental Noise Guideline NPC-300, ‘’Noise Assessment Criteria for Stationary Sources
and for Land Use Planning’’, August 2013.
ISO-9613-1. Acoustics – Attenuation of Sound during propagation outdoors.
Calculation of the absorption of sound by the atmosphere.
Part 1 –
ISO-9613-2. Acoustics – Attenuation of Sound during propagation outdoors. Part 2 – General
method of calculation.
Ontario Ministry of the Environment (MOE), “Basic Comprehensive Certificates of Approval User
Guide”, Version 2.0, April 2004
Ontario Ministry of the Environment (MOE), “Guide for Applying for Approval (Air & Noise)
s.9 EPA”, February 2005.
Ontario Ministry of the Environment (MOE), “Guide for Applying for Approval (Air), Noise and
Vibration”, April 1998.
Ontario Ministry of the Environment Publication NPC-103, "Measurement Procedure", published
under the Model Municipal Noise Control Bylaw, 1977.
Ontario Ministry of the Environment Publication NPC-104, "Sound Level Adjustments",
published under the Model Municipal Noise Control Bylaw, 1977.
Ontario Ministry of the Environment Publication NPC-233, "Information to be Submitted for
Approval of Stationary Sources of Sound", October 1995.
TR1213003
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January 2014
FIGURES
TR1213003
Page 9
POR4
POR5
R8
TR2
POR6
ST
R1
CU12
RTU22
ES4
RTU21
CU11
AIR1
LV1
CU18
CU5
R9
HN
CU23
CU28
HT
CU20
CU29
TR1
BF
CU30
CU24
CU25
LV4
LV3
CU27
LV2
POR7
POR3
POR1
POR2
Aerial Photography from: Google Earth
Site Aerial Map with Points of Reception Location
Drawn by: AS
North
Conestoga Meat Packers Ltd. - Breslau, Ontario
Project No. TR1213003
Scale:
Date:
Figure:
1
1:8,000
January 2014
R8
TR2
ST
R1
CU12
RTU22
ES4
RTU21
CU11
AIR1
LV1
CU18
CU5
R9
HN
CU23
CU28
HT
CU20
CU29
TR1
BF
CU30
CU24
CU25
LV4
LV3
CU27
LV2
Significant Noise Source Location
Drawn by: AS
North
Scale:
Date:
Figure:
2
1:1,500
January 2014
>= 45.0 dBA
>= 50.0 dBA
>= 55.0 dBA
>= 60.0 dBA
>= 65.0 dBA
>= 70.0 dBA
>= 75.0 dBA
>= 80.0 dBA
>= 85.0 dBA
POR4: 35 dBA
Contour Height: 4.5 m
POR5: 48 dBA
R8
TR2
ST
R1
CU12
RTU22
POR6: 34 dBA
ES4
RTU21
CU11
AIR1
LV1
CU18
CU5
R9
HN
CU23
CU28
HT
CU20
CU29
TR1
BF
CU30
CU24
CU25
LV4
LV3
CU27
LV2
POR7: 51 dBA
POR3: 38 dBA
POR1: 45 dBA
POR2: 42 dBA
Noise Contours for Worst-Case Operation
Drawn by: AS
North
Scale:
Date:
Figure:
3
1:8,000
January 2014
>= 55.0 dBA
>= 60.0 dBA
>= 65.0 dBA
>= 70.0 dBA
>= 75.0 dBA
>= 80.0 dBA
>= 85.0 dBA
POR4: 47 dBA
Contour Height: 4.5 m
POR5: 61 dBA
POR6: 37 dBA
POR7: 31 dBA
POR3: 47 dBA
POR1: 30 dBA
POR2: 33 dBA
Noise Contours for Emergency Generator Testing
Drawn by: AS
North
Conestoga Meat Packers Ltd., Breslau, Ontario
Scale:
Date:
Figure:
4
1:8,000
January 2014
January 2014
TABLES
TR1213003
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Table 1: Noise Source Summary
Project:
Location:
Source ID [1]
CMP
Breslau, Ontario
Source Description
Source
Sound
Sound Power
[2]
[3]
Location
Characteristics [4]
Level
Noise Control
Measures [5]
(dBA)
82
85
86
79
83
(I or O)
O
O
O
O
O
(S,Q,I,B,T,C)
S
S
S
S
S
(S,A,B,L,E,O,U)
U
U
U
U
U
AIR1
BF
CU11
CU12
CU18
Air Intake
Barn Fan
Condensing unit 11
Condensing Unit 12&13
Condensing Unit 18
CU20
Condensing Unit 20
85
O
S
U
CU23
Condensing Unit 23
82
O
S
U
CU24
CU24-S1
CU24-S2
CU24-S3
CU24-S4
CU25
CU25-S1
CU25-S2
CU25-S3
Condnsing Unit 24-Top
Condensing Unit 24-Side 1
Condensing Unit 25-Top
Condensingg Unit 25-Side 2
94
91
91
91
91
94
91
91
91
O
O
O
O
O
O
O
O
O
S
S
S
S
S
S
S
S
S
U
U
U
U
U
U
U
U
U
CU25-S4
91
O
S
U
CU27
94
O
S
U
CU27-S1
CU27-S2
CU27-S3
CU27-S4
CU28
CU29
CU30
CU5
ES4
HN
HT
LV1
LV2
LV3
LV4
R1
R2
R3
R4
R5
R6
R7
R8
R9
Condensing Unit 28
Condensing Unit 29
Condensing Unit 30
Condensing Unit 5&6&7
Quickwater boiler exhaust
Hogs Noise
Truck unloading hogs
Blower Louver
Compressor Louver 2
Compressor Louver 3
Compressor Louver 4
Reefer Trailer 1
Reefer Trailer 2
Reefer Trailer 3
Reefer Trailer 4
Reefer Trailer 5
Reefer Trailer 6
Reefer Trailer 7
Reefer Trailer 8
Reefer Trailer 9
91
91
91
91
91
91
91
91
81
86
94
95
85
85
85
86
86
86
86
86
86
86
86
86
O
O
O
O
O
O
O
O
O
O
O
O
O
O
O
O
O
O
O
O
O
O
O
O
S
S
S
S
S
S
S
S
S
S
S
S
S
S
S
S
S
S
S
S
S
S
S
S
U
U
U
U
U
U
U
U
U
U
U
U
U
U
U
U
U
U
U
U
U
U
U
U
Source ID [1]
RTU21
RTU22
ST
Gen
Source Description
make up air unit 21
Air make up unit 22
Sludge Tanks
Generator
Notes to Table:
1.
2.
3.
4.
5.
Sound Power
Source
Sound
[2]
[3]
Level
Location
Characteristics [4]
Noise Control
Measures [5]
(dBA)
(I or O)
(S,Q,I,B,T,C)
(S,A,B,L,E,O,U)
78
78
78
114
O
O
O
O
S
S
S
S
U
U
U
U
Wherever possible, the Source ID matches the identifiers used in the ESDM report.
Sound Power Level of Source, in dBA, not including sound characteristic adjustments per NPC-104.
Values are unadjusted, unmitigated PWLs.
Source Location: O = Outside of building, including the roof, I = Inside of building
Sound Characteristic, per NPC-104
S = Steady
I = Impulsive
T = Tonal
Q = Quasi-Steady Impulsive
B = Buzzing
C = Cyclic
Noise Control Measures To Be Included
S = Silencer/Muffler
L = Lagging
O = other
A = Acoustic lining, plenum
E = acoustic enclosure
U = uncontrolled
B = Barrier
Table 2: Point of Reception Noise Impact
Project:
Location:
CMP
Breslau, Ontario
Point of Reception ID
POR1
Source ID
Source Description
POR2
POR3
Point of Reception Description
Vacant Lot located approximately 160 m
south of the facility
south-east
south
east of the facility
Point of reception coordinates
Z [2]
X
Y
549183
4813218
4.5
Z [2]
X
Y
549318
4813125
4.5
Z [2]
X
Y
549567
4813182
4.5
Distance
(m)
318
276
317
352
314
297
283
224
222
222
225
225
227
225
226
229
228
221
219
219
222
222
288
283
279
302
320
295
280
365
216
223
337
340
342
344
347
349
351
393
319
316
323
387
NA
NA
Point of Reception 1
[1]
Sound Level
Units
[3]
(dBA)
at PoR
20
dBA
25
dBA
20
dBA
16
dBA
17
dBA
24
dBA
21
dBA
35
dBA
35
dBA
35
dBA
26
dBA
21
dBA
34
dBA
29
dBA
35
dBA
19
dBA
18
dBA
35
dBA
35
dBA
35
dBA
25
dBA
21
dBA
22
dBA
18
dBA
21
dBA
24
dBA
19
dBA
25
dBA
29
dBA
32
dBA
25
dBA
27
dBA
9
dBA
9
dBA
10
dBA
11
dBA
10
dBA
10
dBA
10
dBA
19
dBA
12
dBA
5
dBA
0
dBA
11
dBA
21
dBA
5
dBA
Distance
(m)
430
403
411
438
395
380
376
333
332
331
333
334
333
333
332
334
335
326
326
324
326
327
387
382
377
405
433
426
408
409
327
335
437
439
440
441
442
444
444
460
392
444
447
437
NA
NA
[1]
Sound Level
Units
[3]
(dBA)
at PoR
17
dBA
21
dBA
22
dBA
14
dBA
19
dBA
22
dBA
18
dBA
31
dBA
31
dBA
31
dBA
26
dBA
16
dBA
26
dBA
31
dBA
22
dBA
24
dBA
15
dBA
31
dBA
31
dBA
31
dBA
26
dBA
17
dBA
22
dBA
21
dBA
18
dBA
26
dBA
16
dBA
21
dBA
29
dBA
31
dBA
21
dBA
23
dBA
9
dBA
10
dBA
10
dBA
10
dBA
10
dBA
10
dBA
10
dBA
20
dBA
18
dBA
-1
dBA
-4
dBA
10
dBA
15
dBA
2
dBA
Distance
(m)
517
517
473
483
445
435
448
439
440
438
438
440
436
438
435
435
437
430
431
428
428
431
464
460
454
483
519
541
521
398
437
444
504
503
502
501
500
499
498
470
431
551
548
428
NA
NA
POR4
2-storey residential dwelling located
approximately 200 m south of the facility
AIR1
Air Intake
BF
Barn Fan
CU11
Condensing unit 11
CU12
CU18
Condensing Unit 18
CU20
Condensing Unit 20
CU23
Condensing Unit 23
CU24
CU24-S1
CU24-S2
CU24-S3
CU24-S4
CU24
S4
Condensing Unit 24
24-Side
Side 4
CU25
CU25-S1
CU25-S2
CU25-S3
CU25-S4
Condensing
g Unit 25-Side 4
CU27
CU27-S1
CU27-S2
CU27-S3
g Unit 27-Side 4
CU27-S4
Condensing
CU28
Condensing Unit 28
CU29
Condensing Unit 29
CU30
Condensing Unit 30
CU5
ES4
HN
Hogs Noise
HT
LV1
Blower Louver
LV2
Compressor Louver 2
LV4
Compressor Louver 4
R1
Reefer Trailer 1
R2
Reefer Trailer 2
R3
Reefer Trailer 3
R4
Reefer Trailer 4
R5
Reefer Trailer 5
R6
Reefer Trailer 6
R7
Reefer Trailer 7
R8
Reefer Trailer 8
R9
Reefer Trailer 9
RTU21
make up air unit 21
RTU22
Air make up unit 22
ST
Sludge Tanks
TR1
T k Route
Truck
R
1
TR2
Truck Route 2
Notes to Table:
1. Sound Level units
dBA = 1-hour energy equivalent sound level (Leq (1-hr)),
dBAI = Logarithmic mean impulsive noise level (LLM),
) in terms of A
A-Weighted
Weighted decibels incorporating an impulsive time weighting
in terms of A-Weighted decibels.
2. Height above local grade.
3. Noise receptors representative of worst-case potential
impacts have been selected. For the purposes of noise
impact assessment
assessment, the following land uses (existing or
zoned for future use) have been considered:
- permanent , seasonal, or rental residences
- hotels, motels and campgrounds
- nursing / retirement homes
- hospitals and clinics
- schools, universities, libraries and daycare centres
- churches and places of worship
[1]
Sound Level
Units
[3]
(dBA)
at PoR
15
dBA
11
dBA
21
dBA
13
dBA
18
dBA
21
dBA
17
dBA
23
dBA
19
dBA
24
dBA
16
dBA
12
dBA
28
dBA
15
dBA
24
dBA
28
dBA
14
dBA
28
dBA
19
dBA
28
dBA
28
dBA
14
dBA
21
dBA
20
dBA
18
dBA
25
dBA
15
dBA
14
dBA
20
dBA
31
dBA
3
dBA
3
dBA
9
dBA
9
dBA
9
dBA
9
dBA
9
dBA
10
dBA
10
dBA
20
dBA
21
dBA
-7
dBA
-7
dBA
-1
dBA
12
dBA
3
dBA
approximately 400 m north
north-east
east of the
facility
Z [2]
X
Y
549699
4813829
4.5
Distance
(m)
588
640
544
510
526
538
563
624
627
624
621
624
618
621
618
615
618
620
622
620
617
619
571
573
574
571
588
647
640
442
631
629
548
544
541
536
532
528
525
448
511
632
620
430
NA
NA
[1]
Sound Level
Units
[3]
(dBA)
at PoR
14
dBA
5
dBA
20
dBA
13
dBA
17
dBA
19
dBA
14
dBA
24
dBA
12
dBA
14
dBA
14
dBA
25
dBA
24
dBA
13
dBA
18
dBA
25
dBA
25
dBA
24
dBA
12
dBA
18
dBA
25
dBA
25
dBA
16
dBA
16
dBA
16
dBA
23
dBA
13
dBA
-1
dBA
2
dBA
10
dBA
-7
dBA
-5
dBA
14
dBA
14
dBA
13
dBA
13
dBA
12
dBA
10
dBA
9
dBA
20
dBA
16
dBA
10
dBA
10
dBA
-6
dBA
1
dBA
15
dBA
Table 2: Point of Reception Noise Impa
Project:
Location:
CMP
Breslau, Ontario
POR5
POR6
Vacant lot approximately 50 m north
side of the facility
Z [2]
X
Y
549165
4813619
4.5
Source ID
Source Description
AIR1
Air Intake
BF
Barn Fan
CU11
Condensing unit 11
CU12
CU18
Condensing Unit 18
CU20
Condensing Unit 20
CU23
Condensing Unit 23
CU24
CU24-S1
CU24-S2
CU24-S3
CU24-S4
CU24
S4
Condensing Unit 24
24-Side
Side 4
CU25
CU25-S1
CU25-S2
CU25-S3
CU25-S4
Condensing
g Unit 25-Side 4
CU27
CU27-S1
CU27-S2
CU27-S3
g Unit 27-Side 4
CU27-S4
Condensing
CU28
Condensing Unit 28
CU29
Condensing Unit 29
CU30
Condensing Unit 30
CU5
ES4
HN
Hogs Noise
HT
LV1
Blower Louver
LV2
Compressor Louver 2
LV4
Compressor Louver 4
R1
Reefer Trailer 1
R2
Reefer Trailer 2
R3
Reefer Trailer 3
R4
Reefer Trailer 4
R5
Reefer Trailer 5
R6
Reefer Trailer 6
R7
Reefer Trailer 7
R8
Reefer Trailer 8
R9
Reefer Trailer 9
RTU21
make up air unit 21
RTU22
Air make up unit 22
ST
Sludge Tanks
TR1
T k Route
Truck
R
1
TR2
Truck Route 2
Notes to Table:
1. Sound Level units
dBA = 1-hour energy equivalent sound level (Leq (1-hr)),
dBAI = Logarithmic mean impulsive noise level (LLM),
) in
in terms of A-Weighted decibels.
2. Height above local grade.
3. Noise receptors representative of worst-case potential
impacts have been selected. For the purposes of noise
impact assessment
assessment, the following land uses (existing or
zoned for future use) have been considered:
- permanent , seasonal, or rental residences
- hotels, motels and campgrounds
- nursing / retirement homes
- hospitals and clinics
- schools, universities, libraries and daycare centres
- churches and places of worship
Distance
(m)
87
125
120
117
149
159
148
185
185
186
184
183
184
184
185
183
182
191
191
193
191
190
134
139
144
115
85
112
122
226
191
183
90
91
92
93
95
97
98
162
165
89
80
208
NA
NA
[1]
Sound Level
Units
[3]
(dBA)
at PoR
32
dBA
14
dBA
34
dBA
27
dBA
24
dBA
26
dBA
27
dBA
32
dBA
14
dBA
14
dBA
32
dBA
32
dBA
32
dBA
16
dBA
14
dBA
32
dBA
32
dBA
31
dBA
14
dBA
13
dBA
31
dBA
19
dBA
25
dBA
27
dBA
27
dBA
39
dBA
32
dBA
29
dBA
20
dBA
36
dBA
4
dBA
5
dBA
36
dBA
36
dBA
35
dBA
35
dBA
35
dBA
35
dBA
35
dBA
30
dBA
15
dBA
29
dBA
30
dBA
17
dBA
26
dBA
34
dBA
POR7
approximately 690 m north
north-west
west of the
facility
Z [2]
X
Y
548442
4813538
4.5
Distance
(m)
748
714
803
824
834
831
806
776
773
776
778
775
781
778
782
784
780
785
783
786
787
784
790
791
794
779
747
695
711
931
774
769
784
787
791
794
798
802
805
883
854
700
709
923
NA
NA
[1]
Sound Level
Units
[3]
(dBA)
at PoR
11
dBA
15
dBA
16
dBA
8
dBA
12
dBA
15
dBA
11
dBA
22
dBA
22
dBA
12
dBA
11
dBA
22
dBA
22
dBA
14
dBA
9
dBA
12
dBA
22
dBA
22
dBA
22
dBA
12
dBA
6
dBA
18
dBA
16
dBA
16
dBA
16
dBA
20
dBA
11
dBA
16
dBA
23
dBA
17
dBA
13
dBA
15
dBA
11
dBA
12
dBA
15
dBA
15
dBA
15
dBA
15
dBA
15
dBA
14
dBA
-1
dBA
9
dBA
9
dBA
-2
dBA
12
dBA
11
dBA
Vacant Lot located west side of the
facility
Z [2]
X
Y
549102
4813396
4.5
Distance
(m)
166
111
196
233
213
201
175
118
116
118
121
118
125
122
125
128
125
125
123
125
128
125
167
166
164
170
167
119
113
303
113
113
200
204
207
211
215
219
222
292
228
142
152
310
NA
NA
[1]
Sound Level
Units
[3]
(dBA)
at PoR
26
dBA
33
dBA
25
dBA
21
dBA
23
dBA
23
dBA
26
dBA
36
dBA
41
dBA
36
dBA
27
dBA
41
dBA
36
dBA
28
dBA
35
dBA
26
dBA
40
dBA
35
dBA
41
dBA
35
dBA
26
dBA
40
dBA
35
dBA
36
dBA
36
dBA
30
dBA
25
dBA
33
dBA
42
dBA
27
dBA
31
dBA
33
dBA
15
dBA
15
dBA
16
dBA
16
dBA
16
dBA
16
dBA
16
dBA
17
dBA
9
dBA
24
dBA
10
dBA
3
dBA
31
dBA
7
dBA
Table 3: Acoustic Assessment Summary
Project:
Location:
Point of
Reception ID
CMP
Breslau, Ontario
POR1
Two-storey residential dwelling located
approximately 200 m south of the facility
POR2
south of the facility
POR3
south-east of the facility
POR4
approximately 400 m north-east of the
facility
POR5
Vacant lot approximately 50 m north
side of the facility
POR6
approximately 690 m north-west of the
facility
POR7
Vacantt Lot
V
L t located
l t d westt side
id off the
th
facility
Time Period [1]
Daytime
Evening
Night-time
Generator
Daytime
Evening
Night-time
Generator
Daytime
Evening
Night-time
Generator
Daytime
Evening
Night-time
Generator
Daytime
Evening
Night-time
Generator
Daytime
Evening
Night-time
Generator
Daytime
E i
Evening
Night-time
Generator
Total Sound
Level at PoR [2]
Verified by
Acoustic Audit [3]
Performance
Limit [4]
Peformance Limit
Source [4]
Compliance with
Performance Limit
(dBA)
(Yes/No)
No
No
No
No
No
No
No
No
No
No
No
No
No
No
No
No
No
No
No
No
No
No
No
No
No
N
No
No
No
(dBA)
(C / M/ D)
(Yes/No)
45
45
45
30
42
42
42
33
38
38
38
47
35
35
35
47
48
48
48
61
34
34
34
37
51
51
51
31
50
45
45
55
50
45
45
55
50
45
45
55
50
45
45
55
50
45
45
55
50
45
45
55
50
45
45
55
Notes to Table:
1
Daytime occurs from 0700-1900h. Evening occurs from 1900h to 2300h. Night-time occurs from 2300-0700h
2
Worst-case cumulative sound level from all applicable sources operating.
3
Has an acoustic audit (as defined in Publication NPC-233) been conducted with source in place and operating?
4
Applicable worst-case NPC-300 sound level limit.
5
Performance limit (aka guideline limit) based on following:
C = Calculated based on road traffic volumes in compliance with NPC-206 requirements.
M = Measured based on monitoring for a minimum 48 hour period, in accordance with NPC-233 requirements.
D = Default guideline minima per NCP-300, as applicable (e.g., 50 dBA daytime for NPC-300)
D
D
D
D
D
D
D
Yes
Yes
Yes
Yes
Yes
Yes
Yes
Yes
Yes
Yes
Yes
Yes
Yes
Yes
Yes
Yes
Yes
No
No
No
Yes
Yes
Yes
Yes
No
N
No
No
Yes
January 2014
APPENDIX A
ACOUSTIC ASSESSMENT CHECK LIST
TR1213003
Ministry
of the
Environment
Ministère
de
l’Environnement
ACOUSTIC ASSESSMENT REPORT CHECK-LIST
Company Name:
Conestoga Meat Packers Limited
Company Address: 313 Menno Packers Ltd.
Breslau, Ontario
Location of Facility: Same as above
The attached Acoustic Assessment Report was prepared in accordance with the guidance in
the ministry document “Information to be Submitted for Approval of Stationary Sources of
Sound” (NPC 233) dated October 1995 and the minimum required information identified in
the check-list on the reverse of this sheet has been submitted.
Company Contact: Conestoga Meat Packers Limited
Name:
Dan Schwartzentruber
Title:
Maintenance/Facility Manager
Phone Number:
(519) 648 2506 ext 261
Signature:
Date:
Technical Contact: Acoustical Specialist
Name:
Alireza Seifzadeh, MSc
Representing:
AMEC Environment & Infrastructure
Phone Number:
(905) 568 2929 Extn. 4179
Signature:
Date:
January 21, 2014
PIBS 5356e
ACOUSTIC ASSESSMENT REPORT CHECKLIST
Required Information
Submitted
1.0
Introduction (Project Background and Overview)
2.0
3.0
4.0
5.0
6.0
7.0
Explanation/Reference
Yes
Section 1
Facility Description
2.1 Operating hours of facility and significant Noise Sources
Yes
Section 2 & Section 3
2.2
Yes
Figure 2
Noise Source Summary
3.1 Noise Source Summary Table
Yes
Table 1
3.2
Source noise emissions specifications
Yes
Section 3 & Appendix D
3.3
Source Power/capacity ratings
Yes
Appendix D
3.4
Noise control equipment description and acoustical
specifications
Yes
Section 4
Point of Reception Noise Impact Calculations
4.1 Point of Reception Noise Impact Table
Yes
Table 2
4.2
Point(s) of Reception (POR) list and description
Yes
Section 5
4.3
Land-use Zoning Plan
Yes
Appendix B
4.4
Scaled Area Location Plan
Yes
Figure 1
4.5
Procedure used to assess noise impacts at each POR
Yes
Section 7
4.6
List of parameters/assumptions used in calculations
Yes
Section 7/Appendix F
Acoustic Assessment Summary
5.1 Acoustic Assessment Summary Table
Yes
Table 3
5.2
Rationale for selecting applicable noise guideline limits
Yes
Section 6
5.3
Predictable Worst Case Impacts Operating Scenario
Yes
Section 7
Yes
Section 8
Yes
Appendix E
Manufacture’s Noise Specifications
Yes
Appendix D
Calculations
Yes
Appendix D
Yes
Appendix D
Yes
Appendix D
Yes
Appendix D
Yes
Appendix C
Site Plan identifying all significant Noise Sources
Conclusions
6.1 Statement of compliance with the selected noise
performance limits
Appendices (Provide details such as)
Listing of Insignificant Noise Sources
Instrumentation
Meteorology during Sound level Measurements
Raw Data from Measurements
Drawings (Facility/Equipment)
PIBS 5356e
January 2014
APPENDIX B
LAND-USE ZONING MAP
TR1213003
January 2014
APPENDIX C
FACILITY DRAWINGS
TR1213003
LEGEND
EXHAUST FANS
ROOF TOP UNIT
EXHAUST STACK
CONDENSING UNIT
GENERATOR
January 2014
APPENDIX D
NOISE CALCULATIONS AND MEASUREMENT DETAILS
TR1213003
Sound Level Measurement Instrumentation
Equipment sound level measurements at the Conestoga Meat Packers Facility (Breslau) were
conducted by AMEC on October 10, 2013. A Larson Davis Sound Track LxT Type I sound level
meter equipped with a windscreen was used for the measurement. The Model LxT uses a
Larson Davis Model PRMLxT1L preamplifier and a PCB Model 377B02 precision air-condenser
microphone, which have been factory calibrated with the SLM unit. The SLM meets IEC 616721 Type 1 requirements. The sound level meter was field calibrated with a Larson-Davis Model
CA200 precision acoustic calibrator before and after the measurements.
All measurements were conducted in accordance with MOE NPC-103 measurement protocols.
Meters used for short-term measurements were programmed to record 1-second Leq and Lmax.
Summary
Filename
Serial Number
Model
Firmware Version
User
Location
Job Description
Note
Measurement Description
Start
Stop
Duration
Run Time
Pause
Pre Calibration
Post Calibration
Calibration Deviation
Overall Settings
RMS Weight
Peak Weight
Detector
Preamp
Integration Method
OBA Range
OBA Bandwidth
OBA Freq. Weighting
OBA Max Spectrum
Overload
Under Range Peak
Under Range Limit
Noise Floor
Results
LASeq
LASE
EAS
EAS8
EAS40
LZpeak (max)
LASmax
LASmin
SEA
LAS > 85.0 dB (Exceedence Counts / Duration)
LZpeak > 135.0 dB (Exceedence Counts / Duration)
LCSeq
LASeq
LCSeq - LASeq
LAIeq
LAeq
LAIeq - LAeq
# Overloads
Overload Duration
# OBA Overloads
OBA Overload Duration
Dose Settings
Dose Name
Exch. Rate
Threshold
Criterion Level
Criterion Duration
LxT_Data.067
2471
LxT1
1.522
RH
CMP Acoustic Assessment
Truck - refer running
shipping area
2013/10/10 11:23:42
2013/10/10 11:24:29
0:00:46.9
0:00:46.9
0:00:00.0
2013/10/10 11:21:23
None
---
A Weighting
Z Weighting
Slow
PRMLxT1L
Exponential
Normal
1/3 Octave
Z Weighting
Bin Max
121.9 dB
A
77.0
26.0
16.2
76.8
93.5
250.363
153.741
768.705
2013/10/10 11:24:23
2013/10/10 11:23:42
2013/10/10 11:24:27
-99.9
dB
dB
µPa²h
mPa²h
mPa²h
103.4 dB
77.5 dB
76.2 dB
dB
0
0
0
0
0
89.5
76.8
12.7
77.3
76.8
0.5
0
0.0
0
0.0
C
Z
74.0 79.0 dB
25.2 32.0 dB
16.0 21.9 dB
0.0
0.0
0.0
0.0
0.0
s
s
s
s
s
dB
dB
dB
dB
dB
dB
s
s
OSHA 1
5
None
90
8
OSHA 2
5
80
90
8
dB
dB
dB
h
Results
Dose
Projected Dose
TWA (Projected)
TWA (t)
Lep (t)
0.0
16.1
76.8
30.5
48.9
-99.9
-99.9
-99.9
-99.9
48.9
%
%
dB
dB
dB
Statistics
LAS5.00
LAS10.00
LAS33.30
LAS50.00
LAS66.30
LAS90.00
77.3
77.2
77.0
76.8
76.6
76.4
dB
dB
dB
dB
dB
dB
Calibration History
Preamp
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
1/3 Octave
Frequency (Hz)
Overall 1/3 Spectra
Max 1/3 Spectra
Min 1/3 Spectra
2013/10/10
2013/08/15
2013/08/15
2013/07/25
2013/07/25
2013/07/11
2013/07/11
2013/06/28
2013/06/27
2013/06/27
2013/05/03
Date
dB re. 1V/Pa
11:21:20
-27.9
12:57:41
-28.1
12:41:43
-27.9
15:00:18
-28.2
12:47:17
-27.9
14:00:51
-28.2
13:04:13
-27.9
11:57:52
-28.1
10:57:35
-28.1
10:57:11
-28.1
12:42:33
-29.2
6.3
59.3
68.9
48.5
8.0
64.6
74.1
50.2
10.0
62.6
73.0
51.9
6.3
65.1
70.3
69.4
79.0
67.4
78.1
65.8
46.5
43.9
41.9
8.0
62.4
67.7
71.2
71.8
56.4
66.1
79.0
55.9
51.1
47.0
10.0
54.3
72.8
58.0
53.9
58.2
62.2
70.5
63.3
54.6
55.5
12.5
64.9
72.5
69.3
53.0
65.4
69.9
68.2
61.4
61.4
61.3
16.0
51.5
72.0
63.2
64.6
60.1
70.1
63.6
59.2
61.1
57.5
20.0
55.0
68.5
66.4
69.6
65.6
72.9
63.9
50.6
54.9
58.0
25.0
61.1
68.7
71.8
61.8
64.7
62.2
59.5
54.4
53.0
46.5
31.5
68.4
74.5
69.9
61.2
62.9
69.6
62.5
50.9
48.5
60.1
40.0
76.5
64.5
80.9
57.2
64.1
56.8
53.8
54.0
46.1
56.3
50.0
72.5
62.2
66.4
50.7
63.5
54.3
55.8
49.1
59.2
52.8
63.0
68.4
66.7
70.2
50.6
65.9
63.4
57.7
48.4
49.4
62.7
80.0
71.4
58.4
74.3
43.5
67.9
61.3
62.4
45.8
46.9
62.2
100
58.9
59.2
65.0
59.9
62.9
63.4
61.1
50.9
41.7
48.6
125
65.3
61.1
61.2
61.6
71.4
54.8
62.6
49.4
43.0
50.0
160
62.5
61.4
63.0
34.4
75.1
63.9
58.3
46.3
44.2
50.4
200
54.9
56.8
62.7
56.4
68.5
60.2
61.5
46.5
42.9
48.4
250
55.6
59.5
59.6
57.3
67.6
62.3
70.1
45.7
39.3
47.9
315
54.9
55.9
56.0
46.9
66.8
60.3
72.8
38.5
36.7
52.3
400
51.7
55.7
59.0
42.9
66.4
57.7
66.2
33.9
34.0
37.7
500
50.1
48.2
59.4
40.4
67.0
49.8
49.9
34.3
27.8
42.2
630
44.0
39.6
52.1
28.4
58.2
39.6
45.3
30.3
19.3
43.5
800
30.2
32.9
46.8
19.9
45.3
32.9
33.5
28.3
11.8
29.4
1000
94.0
93.7
94.0
93.7
94.0
93.7
94.0
94.0
94.0
95.1
1250
28.9
28.9
31.0
28.4
32.3
28.8
29.4
29.2
29.1
30.0
1600
12.7
11.0
19.9
10.0
22.4
9.6
11.2
7.9
7.8
9.0
2000
35.4
34.6
35.2
35.5
35.3
35.6
35.6
35.3
34.8
36.0
2500
10.4
9.1
11.0
9.7
12.5
10.6
9.9
9.9
11.1
10.7
3150
43.5
43.2
43.7
43.1
43.6
43.2
43.4
43.2
43.4
44.5
4000
12.1
12.7
13.1
11.2
12.1
11.4
11.6
11.5
11.3
12.3
5000
15.6
14.7
16.5
14.3
15.3
16.6
14.9
15.0
15.5
16.0
6300
13.4
13.4
13.5
12.9
13.4
12.9
13.6
13.2
12.6
14.0
8000 10000 12500 16000 20000
14.4 15.2 16.6 17.4
14.7 15.3 16.7 17.5
14.6 16.1 16.6 17.7
14.3 15.3 16.2 17.6
15.1 16.1 16.7 17.7
14.4 15.8 16.4 17.2
14.5 15.1 16.1 17.8
14.7 15.6 16.7 17.3
14.5 15.1 16.4 17.6
15.5 16.3 17.7 18.4
12.5
64.9
73.5
57.1
16.0
64.1
69.7
58.4
20.0
64.5
70.3
58.9
25.0
67.3
79.8
59.1
31.5
71.8
79.0
67.1
40.0
75.9
79.1
71.8
50.0
79.1
81.6
75.2
63.0
83.0
85.8
80.4
80.0
86.2
89.1
78.9
100
70.8
77.0
66.2
125
79.7
81.5
78.8
160
77.8
79.9
76.5
200
76.7
78.9
75.5
250
71.2
73.8
69.5
315
71.4
74.6
68.9
400
67.7
72.0
66.1
500
65.5
68.4
64.0
630
65.5
67.8
63.7
800 1000 1250 1600
67.0 65.9 65.4 63.7
68.5 67.3 66.3 64.7
65.4 64.6 64.6 62.7
2000
64.3
65.2
63.4
2500
63.9
65.0
63.1
3150
60.7
61.9
59.9
4000
59.3
60.6
58.4
5000
54.3
56.8
53.3
6300
51.5
55.3
50.3
8000100001250016000 20000
50.9 48.5 45.6 45.3 40.0
53.7 50.5 47.3 46.1 44.2
49.5 47.4 44.2 43.9 38.3
Summary
Filename
Serial Number
Model
Firmware Version
User
Location
Job Description
Note
Start
Stop
Duration
Run Time
Pause
Pre Calibration
Post Calibration
Overall Settings
RMS Weight
Peak Weight
Detector
Preamp
Integration Method
OBA Range
OBA Bandwidth
OBA Freq. Weighting
OBA Max Spectrum
Overload
Under Range Peak
Under Range Limit
Noise Floor
Results
LASeq
LASE
EAS
EAS8
EAS40
LZpeak (max)
LASmax
LASmin
SEA
LCSeq
LASeq
LCSeq - LASeq
LAIeq
LAeq
LAIeq - LAeq
# Overloads
Overload Duration
# OBA Overloads
Dose Settings
Dose Name
Exch. Rate
Threshold
Criterion Level
Criterion Duration
LxT_Data.068
2471
LxT1
1.522
RH
Slude Tanks
waste water building
2013/10/10 11:36:26
2013/10/10 11:37:12
0:00:45.8
0:00:45.8
0:00:00.0
2013/10/10 11:21:20
None
---
A Weighting
Z Weighting
Slow
PRMLxT1L
Exponential
Normal
1/3 Octave
Z Weighting
Bin Max
121.9 dB
A
77.0
26.0
16.2
68.9
85.5
39.236
24.673
123.363
2013/10/10 11:36:43
2013/10/10 11:37:00
2013/10/10 11:36:47
-99.9
dB
dB
µPa²h
mPa²h
mPa²h
91.6 dB
69.9 dB
68.4 dB
dB
0
0
0
0
0
74.7
68.9
5.8
69.5
68.9
0.6
0
0.0
0
0.0
C
Z
74.0 79.0 dB
25.2 32.0 dB
16.0 21.9 dB
0.0
0.0
0.0
0.0
0.0
s
s
s
s
s
dB
dB
dB
dB
dB
dB
s
s
OSHA 1
5
None
90
8
OSHA 2
5
80
90
8
dB
dB
dB
h
Results
Dose
Projected Dose
TWA (Projected)
TWA (t)
Lep (t)
0.0
5.3
68.9
22.4
40.9
-99.9
-99.9
-99.9
-99.9
40.9
%
%
dB
dB
dB
Statistics
LAS5.00
LAS10.00
LAS33.30
LAS50.00
LAS66.30
LAS90.00
69.4
69.2
68.9
68.8
68.7
68.6
dB
dB
dB
dB
dB
dB
Calibration History
Preamp
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
1/3 Octave
Frequency (Hz)
Overall 1/3 Spectra
Max 1/3 Spectra
Min 1/3 Spectra
2013/10/10
2013/08/15
2013/08/15
2013/07/25
2013/07/25
2013/07/11
2013/07/11
2013/06/28
2013/06/27
2013/06/27
2013/05/03
DatedB re. 1V/Pa
11:21:20
-27.9
12:57:41
-28.1
12:41:43
-27.9
15:00:18
-28.2
12:47:17
-27.9
14:00:51
-28.2
13:04:13
-27.9
11:57:52
-28.1
10:57:35
-28.1
10:57:11
-28.1
12:42:33
-29.2
6.3
63.1
73.8
58.0
8.0
55.7
61.1
43.1
10.0
53.8
59.7
48.8
6.3
65.1
70.3
69.4
79.0
67.4
78.1
65.8
46.5
43.9
41.9
8.0
62.4
67.7
71.2
71.8
56.4
66.1
79.0
55.9
51.1
47.0
10.0
54.3
72.8
58.0
53.9
58.2
62.2
70.5
63.3
54.6
55.5
12.5
64.9
72.5
69.3
53.0
65.4
69.9
68.2
61.4
61.4
61.3
16.0
51.5
72.0
63.2
64.6
60.1
70.1
63.6
59.2
61.1
57.5
20.0
55.0
68.5
66.4
69.6
65.6
72.9
63.9
50.6
54.9
58.0
25.0
61.1
68.7
71.8
61.8
64.7
62.2
59.5
54.4
53.0
46.5
31.5
68.4
74.5
69.9
61.2
62.9
69.6
62.5
50.9
48.5
60.1
40.0
76.5
64.5
80.9
57.2
64.1
56.8
53.8
54.0
46.1
56.3
50.0
72.5
62.2
66.4
50.7
63.5
54.3
55.8
49.1
59.2
52.8
63.0
68.4
66.7
70.2
50.6
65.9
63.4
57.7
48.4
49.4
62.7
80.0
71.4
58.4
74.3
43.5
67.9
61.3
62.4
45.8
46.9
62.2
100
58.9
59.2
65.0
59.9
62.9
63.4
61.1
50.9
41.7
48.6
125
65.3
61.1
61.2
61.6
71.4
54.8
62.6
49.4
43.0
50.0
160
62.5
61.4
63.0
34.4
75.1
63.9
58.3
46.3
44.2
50.4
200
54.9
56.8
62.7
56.4
68.5
60.2
61.5
46.5
42.9
48.4
250
55.6
59.5
59.6
57.3
67.6
62.3
70.1
45.7
39.3
47.9
315
54.9
55.9
56.0
46.9
66.8
60.3
72.8
38.5
36.7
52.3
400
51.7
55.7
59.0
42.9
66.4
57.7
66.2
33.9
34.0
37.7
500
50.1
48.2
59.4
40.4
67.0
49.8
49.9
34.3
27.8
42.2
630
44.0
39.6
52.1
28.4
58.2
39.6
45.3
30.3
19.3
43.5
800
30.2
32.9
46.8
19.9
45.3
32.9
33.5
28.3
11.8
29.4
1000
94.0
93.7
94.0
93.7
94.0
93.7
94.0
94.0
94.0
95.1
1250
28.9
28.9
31.0
28.4
32.3
28.8
29.4
29.2
29.1
30.0
1600
12.7
11.0
19.9
10.0
22.4
9.6
11.2
7.9
7.8
9.0
2000
35.4
34.6
35.2
35.5
35.3
35.6
35.6
35.3
34.8
36.0
2500
10.4
9.1
11.0
9.7
12.5
10.6
9.9
9.9
11.1
10.7
3150
43.5
43.2
43.7
43.1
43.6
43.2
43.4
43.2
43.4
44.5
4000
12.1
12.7
13.1
11.2
12.1
11.4
11.6
11.5
11.3
12.3
5000
15.6
14.7
16.5
14.3
15.3
16.6
14.9
15.0
15.5
16.0
6300
13.4
13.4
13.5
12.9
13.4
12.9
13.6
13.2
12.6
14.0
8000 10000 12500 16000
14.4 15.2 16.6 17.4
14.7 15.3 16.7 17.5
14.6 16.1 16.6 17.7
14.3 15.3 16.2 17.6
15.1 16.1 16.7 17.7
14.4 15.8 16.4 17.2
14.5 15.1 16.1 17.8
14.7 15.6 16.7 17.3
14.5 15.1 16.4 17.6
15.5 16.3 17.7 18.4
12.5
57.7
62.9
51.2
16.0
58.0
63.4
53.1
20.0
60.7
65.5
56.8
25.0
60.3
65.6
56.2
31.5
60.5
67.5
55.6
40.0
62.1
66.3
57.6
50.0
65.9
68.2
62.0
63.0
68.9
72.4
64.6
80.0
63.7
68.2
59.7
100
59.5
62.0
55.1
125
59.4
61.3
56.0
160
62.6
63.7
60.0
200
62.0
65.2
60.5
250
58.0
60.2
54.5
315
61.1
62.4
59.4
400
61.0
62.6
60.0
500
60.4
63.3
59.4
630
60.9
63.6
58.6
800
60.9
64.0
55.6
1000
60.2
61.0
59.5
1250
59.3
63.1
58.4
1600
57.5
58.6
56.8
2000
56.2
59.3
55.5
2500
55.3
58.8
54.5
3150
53.5
54.1
51.8
4000
51.1
51.8
50.5
5000
48.7
49.2
48.0
6300
46.5
47.4
45.9
8000100001250016000 20000
43.7 40.1 35.6 31.2 26.1
45.5 41.0 36.8 33.7 30.2
43.1 39.5 34.9 30.5 25.4
Summary
Filename
Serial Number
Model
Firmware Version
User
Location
Job Description
Note
Start
Stop
Duration
Run Time
Pause
Pre Calibration
Post Calibration
Overall Settings
RMS Weight
Peak Weight
Detector
Preamp
Integration Method
OBA Range
OBA Bandwidth
OBA Freq. Weighting
OBA Max Spectrum
Overload
Under Range Peak
Under Range Limit
Noise Floor
Results
LASeq
LASE
EAS
EAS8
EAS40
LZpeak (max)
LASmax
LASmin
SEA
LCSeq
LASeq
LCSeq - LASeq
LAIeq
LAeq
LAIeq - LAeq
# Overloads
Overload Duration
# OBA Overloads
Dose Settings
Dose Name
Exch. Rate
Threshold
Criterion Level
Criterion Duration
LxT_Data.069
2471
LxT1
1.522
RH
Blower (for aeration)
Waste water building
2013/10/10 11:40:18
2013/10/10 11:41:05
0:00:47.2
0:00:47.2
0:00:00.0
2013/10/10 11:21:20
None
---
A Weighting
Z Weighting
Slow
PRMLxT1L
Exponential
Normal
1/3 Octave
Z Weighting
Bin Max
121.9 dB
A
77.0
26.0
16.2
81.7
98.4
769.959
469.805
2.349
2013/10/10 11:41:04
2013/10/10 11:40:34
2013/10/10 11:40:49
-99.9
dB
dB
µPa²h
mPa²h
Pa²h
99.0 dB
82.1 dB
81.3 dB
dB
0
0
0
0
0
86.6
81.7
5.0
82.0
81.7
0.3
0
0.0
0
0.0
C
Z
74.0 79.0 dB
25.2 32.0 dB
16.0 21.9 dB
0.0
0.0
0.0
0.0
0.0
s
s
s
s
s
dB
dB
dB
dB
dB
dB
s
s
OSHA 1
5
None
90
8
OSHA 2
5
80
90
8
dB
dB
dB
h
Results
Dose
Projected Dose
TWA (Projected)
TWA (t)
Lep (t)
0.1
31.5
81.7
35.4
53.8
0.1
31.5
81.7
35.4
53.8
%
%
dB
dB
dB
Statistics
LAS5.00
LAS10.00
LAS33.30
LAS50.00
LAS66.30
LAS90.00
81.9
81.9
81.7
81.7
81.6
81.4
dB
dB
dB
dB
dB
dB
Calibration History
Preamp
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
1/3 Octave
Frequency (Hz)
Overall 1/3 Spectra
Max 1/3 Spectra
Min 1/3 Spectra
2013/10/10
2013/08/15
2013/08/15
2013/07/25
2013/07/25
2013/07/11
2013/07/11
2013/06/28
2013/06/27
2013/06/27
2013/05/03
DatedB re. 1V/Pa
11:21:20
-27.9
12:57:41
-28.1
12:41:43
-27.9
15:00:18
-28.2
12:47:17
-27.9
14:00:51
-28.2
13:04:13
-27.9
11:57:52
-28.1
10:57:35
-28.1
10:57:11
-28.1
12:42:33
-29.2
6.3
57.5
65.8
50.7
8.0
57.8
65.1
53.3
10.0
54.2
57.2
50.3
6.3
65.1
70.3
69.4
79.0
67.4
78.1
65.8
46.5
43.9
41.9
8.0
62.4
67.7
71.2
71.8
56.4
66.1
79.0
55.9
51.1
47.0
10.0
54.3
72.8
58.0
53.9
58.2
62.2
70.5
63.3
54.6
55.5
12.5
64.9
72.5
69.3
53.0
65.4
69.9
68.2
61.4
61.4
61.3
16.0
51.5
72.0
63.2
64.6
60.1
70.1
63.6
59.2
61.1
57.5
20.0
55.0
68.5
66.4
69.6
65.6
72.9
63.9
50.6
54.9
58.0
25.0
61.1
68.7
71.8
61.8
64.7
62.2
59.5
54.4
53.0
46.5
31.5
68.4
74.5
69.9
61.2
62.9
69.6
62.5
50.9
48.5
60.1
40.0
76.5
64.5
80.9
57.2
64.1
56.8
53.8
54.0
46.1
56.3
50.0
72.5
62.2
66.4
50.7
63.5
54.3
55.8
49.1
59.2
52.8
63.0
68.4
66.7
70.2
50.6
65.9
63.4
57.7
48.4
49.4
62.7
80.0
71.4
58.4
74.3
43.5
67.9
61.3
62.4
45.8
46.9
62.2
100
58.9
59.2
65.0
59.9
62.9
63.4
61.1
50.9
41.7
48.6
125
65.3
61.1
61.2
61.6
71.4
54.8
62.6
49.4
43.0
50.0
160
62.5
61.4
63.0
34.4
75.1
63.9
58.3
46.3
44.2
50.4
200
54.9
56.8
62.7
56.4
68.5
60.2
61.5
46.5
42.9
48.4
250
55.6
59.5
59.6
57.3
67.6
62.3
70.1
45.7
39.3
47.9
315
54.9
55.9
56.0
46.9
66.8
60.3
72.8
38.5
36.7
52.3
400
51.7
55.7
59.0
42.9
66.4
57.7
66.2
33.9
34.0
37.7
500
50.1
48.2
59.4
40.4
67.0
49.8
49.9
34.3
27.8
42.2
630
44.0
39.6
52.1
28.4
58.2
39.6
45.3
30.3
19.3
43.5
800
30.2
32.9
46.8
19.9
45.3
32.9
33.5
28.3
11.8
29.4
1000
94.0
93.7
94.0
93.7
94.0
93.7
94.0
94.0
94.0
95.1
1250
28.9
28.9
31.0
28.4
32.3
28.8
29.4
29.2
29.1
30.0
1600
12.7
11.0
19.9
10.0
22.4
9.6
11.2
7.9
7.8
9.0
2000
35.4
34.6
35.2
35.5
35.3
35.6
35.6
35.3
34.8
36.0
2500
10.4
9.1
11.0
9.7
12.5
10.6
9.9
9.9
11.1
10.7
3150
43.5
43.2
43.7
43.1
43.6
43.2
43.4
43.2
43.4
44.5
4000
12.1
12.7
13.1
11.2
12.1
11.4
11.6
11.5
11.3
12.3
5000
15.6
14.7
16.5
14.3
15.3
16.6
14.9
15.0
15.5
16.0
6300
13.4
13.4
13.5
12.9
13.4
12.9
13.6
13.2
12.6
14.0
8000 10000 12500 16000 20000
14.4 15.2 16.6 17.4
14.7 15.3 16.7 17.5
14.6 16.1 16.6 17.7
14.3 15.3 16.2 17.6
15.1 16.1 16.7 17.7
14.4 15.8 16.4 17.2
14.5 15.1 16.1 17.8
14.7 15.6 16.7 17.3
14.5 15.1 16.4 17.6
15.5 16.3 17.7 18.4
12.5
57.5
61.3
46.9
16.0
60.8
65.0
55.8
20.0
69.3
72.6
67.2
25.0
58.0
62.7
54.8
31.5
62.1
66.0
58.7
40.0
66.6
74.9
58.0
50.0
67.8
74.3
61.0
63.0
65.0
68.6
60.3
80.0
68.0
72.4
48.3
100
73.2
75.8
68.1
125
64.9
70.1
59.6
160
80.8
81.7
80.0
200
80.0
80.4
77.9
250
68.0
69.4
62.0
315
74.5
75.5
68.8
400
75.9
77.0
74.4
500
76.6
78.0
71.4
630
71.5
73.5
70.5
800 1000 1250 1600
71.8 70.7 72.4 71.0
75.8 76.8 74.0 72.1
70.6 68.3 70.4 68.6
2000
71.1
74.0
70.1
2500
63.8
64.5
62.1
3150
60.0
61.3
57.8
4000
56.4
57.7
55.7
5000
53.3
54.0
52.4
6300
53.3
54.1
52.3
8000100001250016000 20000
48.9 45.9 41.8 37.5 32.3
49.9 46.6 42.4 38.2 33.5
48.1 45.5 41.2 37.2 31.9
Summary
Filename
Serial Number
Model
Firmware Version
User
Location
Job Description
Note
Start
Stop
Duration
Run Time
Pause
Pre Calibration
Post Calibration
Overall Settings
RMS Weight
Peak Weight
Detector
Preamp
Integration Method
OBA Range
OBA Bandwidth
OBA Freq. Weighting
OBA Max Spectrum
Overload
Under Range Peak
Under Range Limit
Noise Floor
Results
LASeq
LASE
EAS
EAS8
EAS40
LZpeak (max)
LASmax
LASmin
SEA
LCSeq
LASeq
LCSeq - LASeq
LAIeq
LAeq
LAIeq - LAeq
# Overloads
Overload Duration
# OBA Overloads
Dose Settings
Dose Name
Exch. Rate
Threshold
Criterion Level
Criterion Duration
LxT_Data.070
2471
LxT1
1.522
RH
Barn fans
for hogs on trucks
2013/10/10 11:51:33
2013/10/10 11:52:19
0:00:45.8
0:00:45.8
0:00:00.0
2013/10/10 11:21:20
None
---
A Weighting
Z Weighting
Slow
PRMLxT1L
Exponential
Normal
1/3 Octave
Z Weighting
Bin Max
121.9 dB
A
77.0
26.0
16.2
71.5
88.2
72.702
45.716
228.581
2013/10/10 11:51:34
2013/10/10 11:52:04
2013/10/10 11:51:54
-99.9
dB
dB
µPa²h
mPa²h
mPa²h
110.7 dB
75.0 dB
69.7 dB
dB
0
0
0
0
0
83.8
71.5
12.3
73.8
71.5
2.3
0
0.0
0
0.0
C
Z
74.0 79.0 dB
25.2 32.0 dB
16.0 21.9 dB
0.0
0.0
0.0
0.0
0.0
s
s
s
s
s
dB
dB
dB
dB
dB
dB
s
s
OSHA 1
5
None
90
8
OSHA 2
5
80
90
8
dB
dB
dB
h
Results
Dose
Projected Dose
TWA (Projected)
TWA (t)
Lep (t)
0.0
7.7
71.5
25.0
43.6
-99.9
-99.9
-99.9
-99.9
43.6
%
%
dB
dB
dB
Statistics
LAS5.00
LAS10.00
LAS33.30
LAS50.00
LAS66.30
LAS90.00
73.1
72.4
71.7
71.4
71.1
70.5
dB
dB
dB
dB
dB
dB
Calibration History
Preamp
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
1/3 Octave
Frequency (Hz)
Overall 1/3 Spectra
Max 1/3 Spectra
Min 1/3 Spectra
2013/10/10
2013/08/15
2013/08/15
2013/07/25
2013/07/25
2013/07/11
2013/07/11
2013/06/28
2013/06/27
2013/06/27
2013/05/03
DatedB re. 1V/Pa
11:21:20
-27.9
12:57:41
-28.1
12:41:43
-27.9
15:00:18
-28.2
12:47:17
-27.9
14:00:51
-28.2
13:04:13
-27.9
11:57:52
-28.1
10:57:35
-28.1
10:57:11
-28.1
12:42:33
-29.2
6.3
89.1
94.1
52.2
8.0
89.1
95.3
64.5
10.0
86.4
90.7
73.9
6.3
65.1
70.3
69.4
79.0
67.4
78.1
65.8
46.5
43.9
41.9
8.0
62.4
67.7
71.2
71.8
56.4
66.1
79.0
55.9
51.1
47.0
10.0
54.3
72.8
58.0
53.9
58.2
62.2
70.5
63.3
54.6
55.5
12.5
64.9
72.5
69.3
53.0
65.4
69.9
68.2
61.4
61.4
61.3
16.0
51.5
72.0
63.2
64.6
60.1
70.1
63.6
59.2
61.1
57.5
20.0
55.0
68.5
66.4
69.6
65.6
72.9
63.9
50.6
54.9
58.0
25.0
61.1
68.7
71.8
61.8
64.7
62.2
59.5
54.4
53.0
46.5
31.5
68.4
74.5
69.9
61.2
62.9
69.6
62.5
50.9
48.5
60.1
40.0
76.5
64.5
80.9
57.2
64.1
56.8
53.8
54.0
46.1
56.3
50.0
72.5
62.2
66.4
50.7
63.5
54.3
55.8
49.1
59.2
52.8
63.0
68.4
66.7
70.2
50.6
65.9
63.4
57.7
48.4
49.4
62.7
80.0
71.4
58.4
74.3
43.5
67.9
61.3
62.4
45.8
46.9
62.2
100
58.9
59.2
65.0
59.9
62.9
63.4
61.1
50.9
41.7
48.6
125
65.3
61.1
61.2
61.6
71.4
54.8
62.6
49.4
43.0
50.0
160
62.5
61.4
63.0
34.4
75.1
63.9
58.3
46.3
44.2
50.4
200
54.9
56.8
62.7
56.4
68.5
60.2
61.5
46.5
42.9
48.4
250
55.6
59.5
59.6
57.3
67.6
62.3
70.1
45.7
39.3
47.9
315
54.9
55.9
56.0
46.9
66.8
60.3
72.8
38.5
36.7
52.3
400
51.7
55.7
59.0
42.9
66.4
57.7
66.2
33.9
34.0
37.7
500
50.1
48.2
59.4
40.4
67.0
49.8
49.9
34.3
27.8
42.2
630
44.0
39.6
52.1
28.4
58.2
39.6
45.3
30.3
19.3
43.5
800
30.2
32.9
46.8
19.9
45.3
32.9
33.5
28.3
11.8
29.4
1000
94.0
93.7
94.0
93.7
94.0
93.7
94.0
94.0
94.0
95.1
1250
28.9
28.9
31.0
28.4
32.3
28.8
29.4
29.2
29.1
30.0
1600
12.7
11.0
19.9
10.0
22.4
9.6
11.2
7.9
7.8
9.0
2000
35.4
34.6
35.2
35.5
35.3
35.6
35.6
35.3
34.8
36.0
2500
10.4
9.1
11.0
9.7
12.5
10.6
9.9
9.9
11.1
10.7
3150
43.5
43.2
43.7
43.1
43.6
43.2
43.4
43.2
43.4
44.5
4000
12.1
12.7
13.1
11.2
12.1
11.4
11.6
11.5
11.3
12.3
5000
15.6
14.7
16.5
14.3
15.3
16.6
14.9
15.0
15.5
16.0
6300
13.4
13.4
13.5
12.9
13.4
12.9
13.6
13.2
12.6
14.0
8000 10000 12500 16000 20000
14.4 15.2 16.6 17.4
14.7 15.3 16.7 17.5
14.6 16.1 16.6 17.7
14.3 15.3 16.2 17.6
15.1 16.1 16.7 17.7
14.4 15.8 16.4 17.2
14.5 15.1 16.1 17.8
14.7 15.6 16.7 17.3
14.5 15.1 16.4 17.6
15.5 16.3 17.7 18.4
12.5
85.8
90.1
76.5
16.0
83.3
87.7
77.1
20.0
81.9
88.0
73.9
25.0
79.4
84.1
62.4
31.5
77.6
82.0
71.4
40.0
74.9
79.3
64.3
50.0
73.0
76.2
70.0
63.0
70.9
73.7
64.3
80.0
69.5
72.6
64.0
100
68.5
70.5
66.4
125
68.5
70.3
65.5
160
66.0
67.5
63.9
200
65.1
66.4
55.8
250
62.3
64.4
59.9
315
62.5
64.0
60.7
400
64.7
65.8
62.6
500
63.3
65.6
62.3
630
62.2
65.9
60.9
800 1000 1250 1600
64.5 62.7 62.3 61.9
71.0 69.3 66.1 64.2
60.0 61.2 61.0 59.4
2000
62.2
64.2
61.3
2500
60.8
63.2
59.8
3150
58.3
60.1
57.3
4000
55.1
56.1
54.1
5000
51.9
52.7
50.1
6300
49.6
50.6
48.9
8000100001250016000 20000
46.7 43.6 40.7 38.8 36.2
47.1 44.2 41.6 39.6 39.0
46.1 43.0 40.1 38.1 35.4
Summary
Filename
Serial Number
Model
Firmware Version
User
Location
Job Description
Note
Start
Stop
Duration
Run Time
Pause
Pre Calibration
Post Calibration
Overall Settings
RMS Weight
Peak Weight
Detector
Preamp
Integration Method
OBA Range
OBA Bandwidth
OBA Freq. Weighting
OBA Max Spectrum
Overload
Under Range Peak
Under Range Limit
Noise Floor
Results
LASeq
LASE
EAS
EAS8
EAS40
LZpeak (max)
LASmax
LASmin
SEA
LCSeq
LASeq
LCSeq - LASeq
LAIeq
LAeq
LAIeq - LAeq
# Overloads
Overload Duration
# OBA Overloads
Dose Settings
Dose Name
Exch. Rate
Threshold
Criterion Level
Criterion Duration
LxT_Data.071
2471
LxT1
1.522
RH
RTU21 - Make up air unit
barn
2013/10/10 11:59:16
2013/10/10 12:00:02
0:00:46.0
0:00:46.0
0:00:00.0
2013/10/10 11:21:20
None
---
A Weighting
Z Weighting
Slow
PRMLxT1L
Exponential
Normal
1/3 Octave
Z Weighting
Bin Max
121.9 dB
A
77.0
26.0
16.2
65.5
82.1
17.951
11.239
56.196
2013/10/10 11:59:16
2013/10/10 11:59:48
2013/10/10 11:59:16
-99.9
dB
dB
µPa²h
mPa²h
mPa²h
95.7 dB
70.1 dB
62.5 dB
dB
0
0
0
0
0
77.5
65.5
12.0
65.9
65.5
0.4
0
0.0
0
0.0
C
Z
74.0 79.0 dB
25.2 32.0 dB
16.0 21.9 dB
0.0
0.0
0.0
0.0
0.0
s
s
s
s
s
dB
dB
dB
dB
dB
dB
s
s
OSHA 1 OSHA 2
5
5 dB
None
80 dB
90
90 dB
8
8 h
Results
Dose
Projected Dose
TWA (Projected)
TWA (t)
Lep (t)
0.0
3.3
65.3
18.9
37.5
Statistics
LAS5.00
LAS10.00
LAS33.30
LAS50.00
LAS66.30
LAS90.00
68.8
66.9
65.1
64.7
64.6
64.5
-99.9
-99.9
-99.9
-99.9
37.5
dB
dB
dB
dB
dB
dB
%
%
dB
dB
dB
Calibration History
Preamp
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
1/3 Octave
Frequency (Hz)
Overall 1/3 Spectra
Max 1/3 Spectra
Min 1/3 Spectra
2013/10/10
2013/08/15
2013/08/15
2013/07/25
2013/07/25
2013/07/11
2013/07/11
2013/06/28
2013/06/27
2013/06/27
2013/05/03
Date
dB re. 1V/Pa
11:21:20
-27.9
12:57:41
-28.1
12:41:43
-27.9
15:00:18
-28.2
12:47:17
-27.9
14:00:51
-28.2
13:04:13
-27.9
11:57:52
-28.1
10:57:35
-28.1
10:57:11
-28.1
12:42:33
-29.2
6.3
61.1
65.3
56.5
8.0
64.3
67.4
59.3
10.0
64.6
69.9
59.5
6.3
65.1
70.3
69.4
79.0
67.4
78.1
65.8
46.5
43.9
41.9
8.0
62.4
67.7
71.2
71.8
56.4
66.1
79.0
55.9
51.1
47.0
10.0
54.3
72.8
58.0
53.9
58.2
62.2
70.5
63.3
54.6
55.5
12.5
64.9
72.5
69.3
53.0
65.4
69.9
68.2
61.4
61.4
61.3
16.0
51.5
72.0
63.2
64.6
60.1
70.1
63.6
59.2
61.1
57.5
20.0
55.0
68.5
66.4
69.6
65.6
72.9
63.9
50.6
54.9
58.0
25.0
61.1
68.7
71.8
61.8
64.7
62.2
59.5
54.4
53.0
46.5
31.5
68.4
74.5
69.9
61.2
62.9
69.6
62.5
50.9
48.5
60.1
40.0
76.5
64.5
80.9
57.2
64.1
56.8
53.8
54.0
46.1
56.3
50.0
72.5
62.2
66.4
50.7
63.5
54.3
55.8
49.1
59.2
52.8
63.0
68.4
66.7
70.2
50.6
65.9
63.4
57.7
48.4
49.4
62.7
80.0
71.4
58.4
74.3
43.5
67.9
61.3
62.4
45.8
46.9
62.2
100
58.9
59.2
65.0
59.9
62.9
63.4
61.1
50.9
41.7
48.6
125
65.3
61.1
61.2
61.6
71.4
54.8
62.6
49.4
43.0
50.0
160
62.5
61.4
63.0
34.4
75.1
63.9
58.3
46.3
44.2
50.4
200
54.9
56.8
62.7
56.4
68.5
60.2
61.5
46.5
42.9
48.4
250
55.6
59.5
59.6
57.3
67.6
62.3
70.1
45.7
39.3
47.9
315
54.9
55.9
56.0
46.9
66.8
60.3
72.8
38.5
36.7
52.3
400
51.7
55.7
59.0
42.9
66.4
57.7
66.2
33.9
34.0
37.7
500
50.1
48.2
59.4
40.4
67.0
49.8
49.9
34.3
27.8
42.2
630
44.0
39.6
52.1
28.4
58.2
39.6
45.3
30.3
19.3
43.5
800
30.2
32.9
46.8
19.9
45.3
32.9
33.5
28.3
11.8
29.4
1000
94.0
93.7
94.0
93.7
94.0
93.7
94.0
94.0
94.0
95.1
1250
28.9
28.9
31.0
28.4
32.3
28.8
29.4
29.2
29.1
30.0
1600
12.7
11.0
19.9
10.0
22.4
9.6
11.2
7.9
7.8
9.0
2000
35.4
34.6
35.2
35.5
35.3
35.6
35.6
35.3
34.8
36.0
2500
10.4
9.1
11.0
9.7
12.5
10.6
9.9
9.9
11.1
10.7
3150
43.5
43.2
43.7
43.1
43.6
43.2
43.4
43.2
43.4
44.5
4000
12.1
12.7
13.1
11.2
12.1
11.4
11.6
11.5
11.3
12.3
5000
15.6
14.7
16.5
14.3
15.3
16.6
14.9
15.0
15.5
16.0
6300
13.4
13.4
13.5
12.9
13.4
12.9
13.6
13.2
12.6
14.0
8000 10000 12500 16000 20000
14.4 15.2 16.6 17.4
14.7 15.3 16.7 17.5
14.6 16.1 16.6 17.7
14.3 15.3 16.2 17.6
15.1 16.1 16.7 17.7
14.4 15.8 16.4 17.2
14.5 15.1 16.1 17.8
14.7 15.6 16.7 17.3
14.5 15.1 16.4 17.6
15.5 16.3 17.7 18.4
12.5
64.9
68.1
61.3
16.0
67.2
71.1
64.2
20.0
67.3
70.7
64.1
25.0
68.6
71.7
61.5
31.5
70.7
73.5
66.9
40.0
70.0
72.3
66.4
50.0
72.7
75.1
70.7
63.0
71.0
73.4
68.6
80.0
67.2
69.0
60.8
100
65.4
68.8
63.0
125
59.7
65.8
58.0
160
59.2
61.6
57.2
200
57.9
61.7
53.0
250
56.4
59.0
47.2
315
51.4
56.5
47.5
400
54.3
59.8
48.0
500
54.8
60.7
53.2
630
55.8
58.7
54.5
800
56.6
62.3
50.5
1000
57.4
63.4
55.5
1250
56.0
62.6
53.0
1600
55.0
60.0
51.0
2000
53.4
57.3
51.9
2500
53.1
56.9
48.6
3150
52.2
55.0
47.0
4000
48.8
51.0
47.5
5000
45.4
48.3
44.5
6300
44.0
45.2
43.4
8000100001250016000 20000
41.2 36.7 32.5 30.0 25.7
43.1 39.0 35.7 33.0 30.1
40.6 35.8 30.4 29.3 24.8
Summary
Filename
Serial Number
Model
Firmware Version
User
Location
Job Description
Note
Start
Stop
Duration
Run Time
Pause
Pre Calibration
Post Calibration
Overall Settings
RMS Weight
Peak Weight
Detector
Preamp
Integration Method
OBA Range
OBA Bandwidth
OBA Freq. Weighting
OBA Max Spectrum
Overload
Under Range Peak
Under Range Limit
Noise Floor
Results
LASeq
LASE
EAS
EAS8
EAS40
LZpeak (max)
LASmax
LASmin
SEA
LCSeq
LASeq
LCSeq - LASeq
LAIeq
LAeq
LAIeq - LAeq
# Overloads
Overload Duration
# OBA Overloads
Dose Settings
Dose Name
Exch. Rate
Threshold
Criterion Level
Criterion Duration
LxT_Data.072
2471
LxT1
1.522
RH
Trauck Backing
to unload hogs
2013/10/10 12:07:26
2013/10/10 12:08:13
0:00:46.3
0:00:46.3
0:00:00.0
2013/10/10 11:21:20
None
---
A Weighting
Z Weighting
Slow
PRMLxT1L
Exponential
Normal
1/3 Octave
Z Weighting
Bin Max
121.9 dB
A
77.0
26.0
16.2
73.7
90.4
121.876
75.811
379.053
2013/10/10 12:08:11
2013/10/10 12:08:11
2013/10/10 12:07:26
-99.9
dB
dB
µPa²h
mPa²h
mPa²h
105.8 dB
86.6 dB
61.9 dB
dB
1
0
0
0
0
79.7
73.7
6.0
79.4
74.2
5.2
0
0.0
0
0.0
C
Z
74.0 79.0 dB
25.2 32.0 dB
16.0 21.9 dB
1.3
0.0
0.0
0.0
0.0
s
s
s
s
s
dB
dB
dB
dB
dB
dB
s
s
OSHA 1
5
None
90
8
OSHA 2
5
80
90
8
dB
dB
dB
h
Results
Dose
Projected Dose
TWA (Projected)
TWA (t)
Lep (t)
0.0
8.8
72.5
26.1
45.8
0.0
1.8
61.1
14.7
45.8
%
%
dB
dB
dB
Statistics
LAS5.00
LAS10.00
LAS33.30
LAS50.00
LAS66.30
LAS90.00
72.9
72.6
71.6
71.0
70.6
70.1
dB
dB
dB
dB
dB
dB
Calibration History
Preamp
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
1/3 Octave
Frequency (Hz)
Overall 1/3 Spectra
Max 1/3 Spectra
Min 1/3 Spectra
2013/10/10
2013/08/15
2013/08/15
2013/07/25
2013/07/25
2013/07/11
2013/07/11
2013/06/28
2013/06/27
2013/06/27
2013/05/03
Date dB re. 1V/Pa
11:21:20
-27.9
12:57:41
-28.1
12:41:43
-27.9
15:00:18
-28.2
12:47:17
-27.9
14:00:51
-28.2
13:04:13
-27.9
11:57:52
-28.1
10:57:35
-28.1
10:57:11
-28.1
12:42:33
-29.2
6.3
60.9
70.0
48.3
8.0
62.7
76.2
51.6
10.0
59.0
67.5
51.9
6.3
65.1
70.3
69.4
79.0
67.4
78.1
65.8
46.5
43.9
41.9
8.0
62.4
67.7
71.2
71.8
56.4
66.1
79.0
55.9
51.1
47.0
10.0
54.3
72.8
58.0
53.9
58.2
62.2
70.5
63.3
54.6
55.5
12.5
64.9
72.5
69.3
53.0
65.4
69.9
68.2
61.4
61.4
61.3
16.0
51.5
72.0
63.2
64.6
60.1
70.1
63.6
59.2
61.1
57.5
20.0
55.0
68.5
66.4
69.6
65.6
72.9
63.9
50.6
54.9
58.0
25.0
61.1
68.7
71.8
61.8
64.7
62.2
59.5
54.4
53.0
46.5
31.5
68.4
74.5
69.9
61.2
62.9
69.6
62.5
50.9
48.5
60.1
40.0
76.5
64.5
80.9
57.2
64.1
56.8
53.8
54.0
46.1
56.3
50.0
72.5
62.2
66.4
50.7
63.5
54.3
55.8
49.1
59.2
52.8
63.0
68.4
66.7
70.2
50.6
65.9
63.4
57.7
48.4
49.4
62.7
80.0
71.4
58.4
74.3
43.5
67.9
61.3
62.4
45.8
46.9
62.2
100
58.9
59.2
65.0
59.9
62.9
63.4
61.1
50.9
41.7
48.6
125
65.3
61.1
61.2
61.6
71.4
54.8
62.6
49.4
43.0
50.0
160
62.5
61.4
63.0
34.4
75.1
63.9
58.3
46.3
44.2
50.4
200
54.9
56.8
62.7
56.4
68.5
60.2
61.5
46.5
42.9
48.4
250
55.6
59.5
59.6
57.3
67.6
62.3
70.1
45.7
39.3
47.9
315
54.9
55.9
56.0
46.9
66.8
60.3
72.8
38.5
36.7
52.3
400
51.7
55.7
59.0
42.9
66.4
57.7
66.2
33.9
34.0
37.7
500
50.1
48.2
59.4
40.4
67.0
49.8
49.9
34.3
27.8
42.2
630
44.0
39.6
52.1
28.4
58.2
39.6
45.3
30.3
19.3
43.5
800
30.2
32.9
46.8
19.9
45.3
32.9
33.5
28.3
11.8
29.4
1000
94.0
93.7
94.0
93.7
94.0
93.7
94.0
94.0
94.0
95.1
1250
28.9
28.9
31.0
28.4
32.3
28.8
29.4
29.2
29.1
30.0
1600
12.7
11.0
19.9
10.0
22.4
9.6
11.2
7.9
7.8
9.0
2000
35.4
34.6
35.2
35.5
35.3
35.6
35.6
35.3
34.8
36.0
2500
10.4
9.1
11.0
9.7
12.5
10.6
9.9
9.9
11.1
10.7
3150
43.5
43.2
43.7
43.1
43.6
43.2
43.4
43.2
43.4
44.5
4000
12.1
12.7
13.1
11.2
12.1
11.4
11.6
11.5
11.3
12.3
5000
15.6
14.7
16.5
14.3
15.3
16.6
14.9
15.0
15.5
16.0
6300
13.4
13.4
13.5
12.9
13.4
12.9
13.6
13.2
12.6
14.0
8000 10000 12500 16000 20000
14.4 15.2 16.6 17.4
14.7 15.3 16.7 17.5
14.6 16.1 16.6 17.7
14.3 15.3 16.2 17.6
15.1 16.1 16.7 17.7
14.4 15.8 16.4 17.2
14.5 15.1 16.1 17.8
14.7 15.6 16.7 17.3
14.5 15.1 16.4 17.6
15.5 16.3 17.7 18.4
12.5
62.2
68.6
56.6
16.0
62.3
69.8
55.8
20.0
62.1
67.9
57.5
25.0
61.8
70.3
56.6
31.5
71.0
74.7
58.1
40.0
68.4
74.0
63.0
50.0
75.3
82.5
63.3
63.0
73.5
78.5
62.2
80.0
67.8
71.6
63.7
100
67.1
70.6
63.5
125
65.8
68.1
62.2
160
62.7
66.0
56.7
200
61.1
66.3
56.5
250
59.2
63.3
55.8
315
60.5
67.2
56.5
400
62.2
67.6
56.6
500
62.8
70.4
58.1
630
63.2
71.1
53.3
800 1000 1250 1600
64.1 64.2 63.5 63.3
71.7 73.8 76.0 77.1
54.4 58.8 52.7 49.8
2000
62.3
76.2
53.4
2500
62.2
76.3
48.6
3150
61.6
76.0
47.6
4000
60.3
75.7
44.8
5000
58.8
74.4
42.0
6300
57.4
73.1
39.8
8000100001250016000 20000
58.9 53.4 49.6 47.1 41.8
75.1 69.2 65.4 63.0 57.7
36.5 33.2 29.7 24.0 21.7
Summary
Filename
Serial Number
Model
Firmware Version
User
Location
Job Description
Note
Start
Stop
Duration
Run Time
Pause
Pre Calibration
Post Calibration
Overall Settings
RMS Weight
Peak Weight
Detector
Preamp
Integration Method
OBA Range
OBA Bandwidth
OBA Freq. Weighting
OBA Max Spectrum
Overload
Under Range Peak
Under Range Limit
Noise Floor
Results
LASeq
LASE
EAS
EAS8
EAS40
LZpeak (max)
LASmax
LASmin
SEA
LCSeq
LASeq
LCSeq - LASeq
LAIeq
LAeq
LAIeq - LAeq
# Overloads
Overload Duration
# OBA Overloads
Dose Settings
Dose Name
Exch. Rate
Threshold
Criterion Level
Criterion Duration
LxT_Data.073
2471
LxT1
1.522
RH
Truck Parked/Idle
waiting to unload hogs at barn
2013/10/10 12:11:25
2013/10/10 12:11:56
0:00:30.9
0:00:30.9
0:00:00.0
2013/10/10 11:21:20
None
---
A Weighting
Z Weighting
Slow
PRMLxT1L
Exponential
Normal
1/3 Octave
Z Weighting
Bin Max
121.9 dB
A
C
Z
77.0
74.0 79.0 dB
26.0
25.2 32.0 dB
16.2
16.0 21.9 dB
70.8
85.7
41.590
38.764
193.818
2013/10/10 12:11:53
2013/10/10 12:11:30
2013/10/10 12:11:45
-99.9
dB
dB
µPa²h
mPa²h
mPa²h
104.9 dB
77.5 dB
66.7 dB
dB
0
0
0
0
0
77.2
70.8
6.3
74.6
70.8
3.8
0
0.0
0
0.0
0.0
0.0
0.0
0.0
0.0
s
s
s
s
s
dB
dB
dB
dB
dB
dB
s
s
OSHA 1 OSHA 2
5
5 dB
None
80 dB
90
90 dB
8
8 h
Results
Dose
Projected Dose
TWA (Projected)
TWA (t)
Lep (t)
0.0
6.7
70.5
21.1
41.1
Statistics
LAS5.00
LAS10.00
LAS33.30
LAS50.00
LAS66.30
LAS90.00
74.3
73.5
71.8
69.2
67.8
66.9
-99.9
-99.9
-99.9
-99.9
41.1
dB
dB
dB
dB
dB
dB
%
%
dB
dB
dB
Calibration History
Preamp
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
1/3 Octave
Frequency (Hz)
Overall 1/3 Spectra
Max 1/3 Spectra
Min 1/3 Spectra
2013/10/10
2013/08/15
2013/08/15
2013/07/25
2013/07/25
2013/07/11
2013/07/11
2013/06/28
2013/06/27
2013/06/27
2013/05/03
Date
dB re. 1V/Pa
11:21:20
-27.9
12:57:41
-28.1
12:41:43
-27.9
15:00:18
-28.2
12:47:17
-27.9
14:00:51
-28.2
13:04:13
-27.9
11:57:52
-28.1
10:57:35
-28.1
10:57:11
-28.1
12:42:33
-29.2
6.3
63.7
73.1
53.7
8.0
64.1
75.1
55.5
10.0
59.9
67.1
54.0
6.3
65.1
70.3
69.4
79.0
67.4
78.1
65.8
46.5
43.9
41.9
8.0
62.4
67.7
71.2
71.8
56.4
66.1
79.0
55.9
51.1
47.0
10.0
54.3
72.8
58.0
53.9
58.2
62.2
70.5
63.3
54.6
55.5
12.5
64.9
72.5
69.3
53.0
65.4
69.9
68.2
61.4
61.4
61.3
16.0
51.5
72.0
63.2
64.6
60.1
70.1
63.6
59.2
61.1
57.5
20.0
55.0
68.5
66.4
69.6
65.6
72.9
63.9
50.6
54.9
58.0
25.0
61.1
68.7
71.8
61.8
64.7
62.2
59.5
54.4
53.0
46.5
31.5
68.4
74.5
69.9
61.2
62.9
69.6
62.5
50.9
48.5
60.1
40.0
76.5
64.5
80.9
57.2
64.1
56.8
53.8
54.0
46.1
56.3
50.0
72.5
62.2
66.4
50.7
63.5
54.3
55.8
49.1
59.2
52.8
63.0
68.4
66.7
70.2
50.6
65.9
63.4
57.7
48.4
49.4
62.7
80.0
71.4
58.4
74.3
43.5
67.9
61.3
62.4
45.8
46.9
62.2
100
58.9
59.2
65.0
59.9
62.9
63.4
61.1
50.9
41.7
48.6
125
65.3
61.1
61.2
61.6
71.4
54.8
62.6
49.4
43.0
50.0
160
62.5
61.4
63.0
34.4
75.1
63.9
58.3
46.3
44.2
50.4
200
54.9
56.8
62.7
56.4
68.5
60.2
61.5
46.5
42.9
48.4
250
55.6
59.5
59.6
57.3
67.6
62.3
70.1
45.7
39.3
47.9
315
54.9
55.9
56.0
46.9
66.8
60.3
72.8
38.5
36.7
52.3
400
51.7
55.7
59.0
42.9
66.4
57.7
66.2
33.9
34.0
37.7
500
50.1
48.2
59.4
40.4
67.0
49.8
49.9
34.3
27.8
42.2
630
44.0
39.6
52.1
28.4
58.2
39.6
45.3
30.3
19.3
43.5
800
30.2
32.9
46.8
19.9
45.3
32.9
33.5
28.3
11.8
29.4
1000
94.0
93.7
94.0
93.7
94.0
93.7
94.0
94.0
94.0
95.1
1250
28.9
28.9
31.0
28.4
32.3
28.8
29.4
29.2
29.1
30.0
1600
12.7
11.0
19.9
10.0
22.4
9.6
11.2
7.9
7.8
9.0
2000
35.4
34.6
35.2
35.5
35.3
35.6
35.6
35.3
34.8
36.0
2500
10.4
9.1
11.0
9.7
12.5
10.6
9.9
9.9
11.1
10.7
3150
43.5
43.2
43.7
43.1
43.6
43.2
43.4
43.2
43.4
44.5
4000
12.1
12.7
13.1
11.2
12.1
11.4
11.6
11.5
11.3
12.3
5000
15.6
14.7
16.5
14.3
15.3
16.6
14.9
15.0
15.5
16.0
6300
13.4
13.4
13.5
12.9
13.4
12.9
13.6
13.2
12.6
14.0
8000 10000 12500 16000 20000
14.4 15.2 16.6 17.4
14.7 15.3 16.7 17.5
14.6 16.1 16.6 17.7
14.3 15.3 16.2 17.6
15.1 16.1 16.7 17.7
14.4 15.8 16.4 17.2
14.5 15.1 16.1 17.8
14.7 15.6 16.7 17.3
14.5 15.1 16.4 17.6
15.5 16.3 17.7 18.4
12.5
68.9
72.3
67.1
16.0
65.1
80.3
58.2
20.0
65.3
74.2
61.3
25.0
65.6
80.3
55.7
31.5
65.1
73.9
61.1
40.0
64.4
77.8
58.2
50.0
65.0
78.0
58.2
63.0
71.2
73.4
70.0
80.0
64.8
72.9
62.1
100
64.1
68.0
62.2
125
69.6
71.5
64.4
160
61.5
64.1
60.1
200
58.7
60.7
55.6
250
61.3
63.0
54.7
315
59.0
62.4
54.4
400
59.8
64.4
55.1
500
61.7
70.7
53.9
630
61.3
69.6
58.6
800 1000 1250 1600
60.7 66.4 61.4 58.5
67.3 71.8 69.3 67.8
45.5 57.4 55.8 53.5
2000
56.5
63.6
52.9
2500
53.6
61.1
44.7
3150
53.7
61.9
49.0
4000
51.6
62.4
45.2
5000
48.6
57.6
43.7
6300
48.2
59.5
40.0
8000100001250016000 20000
47.7 45.9 44.2 41.2 36.9
58.8 57.7 56.6 53.2 49.5
41.2 40.5 37.5 35.9 30.2
Summary
Filename
Serial Number
Model
Firmware Version
User
Location
Job Description
Note
Start
Stop
Duration
Run Time
Pause
Pre Calibration
Post Calibration
Overall Settings
RMS Weight
Peak Weight
Detector
Preamp
Integration Method
OBA Range
OBA Bandwidth
OBA Freq. Weighting
OBA Max Spectrum
Overload
Under Range Peak
Under Range Limit
Noise Floor
Results
LASeq
LASE
EAS
EAS8
EAS40
LZpeak (max)
LASmax
LASmin
SEA
LCSeq
LASeq
LCSeq - LASeq
LAIeq
LAeq
LAIeq - LAeq
# Overloads
Overload Duration
# OBA Overloads
Dose Settings
Dose Name
Exch. Rate
Threshold
Criterion Level
Criterion Duration
LxT_Data.074
2471
LxT1
1.522
RH
Truck Unloading
Unloading hogs at barn
2013/10/10 12:17:45
2013/10/10 12:18:37
0:00:52.3
0:00:52.3
0:00:00.0
2013/10/10 11:21:20
None
---
A Weighting
Z Weighting
Slow
PRMLxT1L
Exponential
Normal
1/3 Octave
Z Weighting
Bin Max
121.9 dB
A
77.0
26.0
16.2
81.6
98.8
839.265
462.157
2.311
2013/10/10 12:17:59
2013/10/10 12:17:59
2013/10/10 12:18:37
-99.9
dB
dB
µPa²h
mPa²h
Pa²h
106.2 dB
89.8 dB
72.8 dB
dB
3
0
0
0
0
83.7
81.6
2.1
86.2
81.3
4.9
0
0.0
0
0.0
C
Z
74.0 79.0 dB
25.2 32.0 dB
16.0 21.9 dB
8.8
0.0
0.0
0.0
0.0
s
s
s
s
s
dB
dB
dB
dB
dB
dB
s
s
OSHA 1
5
None
90
8
OSHA 2
5
80
90
8
dB
dB
dB
h
Results
Dose
Projected Dose
TWA (Projected)
TWA (t)
Lep (t)
0.1
28.6
81.0
35.4
54.2
0.0
20.0
78.4
32.9
54.2
%
%
dB
dB
dB
Statistics
LAS5.00
LAS10.00
LAS33.30
LAS50.00
LAS66.30
LAS90.00
86.3
85.0
81.7
79.9
77.9
75.2
dB
dB
dB
dB
dB
dB
Calibration History
Preamp
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
1/3 Octave
Frequency (Hz)
Overall 1/3 Spectra
Max 1/3 Spectra
Min 1/3 Spectra
2013/10/10
2013/08/15
2013/08/15
2013/07/25
2013/07/25
2013/07/11
2013/07/11
2013/06/28
2013/06/27
2013/06/27
2013/05/03
DatedB re. 1V/Pa
11:21:20
-27.9
12:57:41
-28.1
12:41:43
-27.9
15:00:18
-28.2
12:47:17
-27.9
14:00:51
-28.2
13:04:13
-27.9
11:57:52
-28.1
10:57:35
-28.1
10:57:11
-28.1
12:42:33
-29.2
6.3
61.2
65.4
54.1
8.0
64.3
69.5
55.5
10.0
59.9
66.0
53.5
6.3
65.1
70.3
69.4
79.0
67.4
78.1
65.8
46.5
43.9
41.9
8.0
62.4
67.7
71.2
71.8
56.4
66.1
79.0
55.9
51.1
47.0
10.0
54.3
72.8
58.0
53.9
58.2
62.2
70.5
63.3
54.6
55.5
12.5
64.9
72.5
69.3
53.0
65.4
69.9
68.2
61.4
61.4
61.3
16.0
51.5
72.0
63.2
64.6
60.1
70.1
63.6
59.2
61.1
57.5
20.0
55.0
68.5
66.4
69.6
65.6
72.9
63.9
50.6
54.9
58.0
25.0
61.1
68.7
71.8
61.8
64.7
62.2
59.5
54.4
53.0
46.5
31.5
68.4
74.5
69.9
61.2
62.9
69.6
62.5
50.9
48.5
60.1
40.0
76.5
64.5
80.9
57.2
64.1
56.8
53.8
54.0
46.1
56.3
50.0
72.5
62.2
66.4
50.7
63.5
54.3
55.8
49.1
59.2
52.8
63.0
68.4
66.7
70.2
50.6
65.9
63.4
57.7
48.4
49.4
62.7
80.0
71.4
58.4
74.3
43.5
67.9
61.3
62.4
45.8
46.9
62.2
100
58.9
59.2
65.0
59.9
62.9
63.4
61.1
50.9
41.7
48.6
125
65.3
61.1
61.2
61.6
71.4
54.8
62.6
49.4
43.0
50.0
160
62.5
61.4
63.0
34.4
75.1
63.9
58.3
46.3
44.2
50.4
200
54.9
56.8
62.7
56.4
68.5
60.2
61.5
46.5
42.9
48.4
250
55.6
59.5
59.6
57.3
67.6
62.3
70.1
45.7
39.3
47.9
315
54.9
55.9
56.0
46.9
66.8
60.3
72.8
38.5
36.7
52.3
400
51.7
55.7
59.0
42.9
66.4
57.7
66.2
33.9
34.0
37.7
500
50.1
48.2
59.4
40.4
67.0
49.8
49.9
34.3
27.8
42.2
630
44.0
39.6
52.1
28.4
58.2
39.6
45.3
30.3
19.3
43.5
800
30.2
32.9
46.8
19.9
45.3
32.9
33.5
28.3
11.8
29.4
1000
94.0
93.7
94.0
93.7
94.0
93.7
94.0
94.0
94.0
95.1
1250
28.9
28.9
31.0
28.4
32.3
28.8
29.4
29.2
29.1
30.0
1600
12.7
11.0
19.9
10.0
22.4
9.6
11.2
7.9
7.8
9.0
2000
35.4
34.6
35.2
35.5
35.3
35.6
35.6
35.3
34.8
36.0
2500
10.4
9.1
11.0
9.7
12.5
10.6
9.9
9.9
11.1
10.7
3150
43.5
43.2
43.7
43.1
43.6
43.2
43.4
43.2
43.4
44.5
4000
12.1
12.7
13.1
11.2
12.1
11.4
11.6
11.5
11.3
12.3
5000
15.6
14.7
16.5
14.3
15.3
16.6
14.9
15.0
15.5
16.0
6300
13.4
13.4
13.5
12.9
13.4
12.9
13.6
13.2
12.6
14.0
8000 10000 12500 16000 20000
14.4 15.2 16.6 17.4
14.7 15.3 16.7 17.5
14.6 16.1 16.6 17.7
14.3 15.3 16.2 17.6
15.1 16.1 16.7 17.7
14.4 15.8 16.4 17.2
14.5 15.1 16.1 17.8
14.7 15.6 16.7 17.3
14.5 15.1 16.4 17.6
15.5 16.3 17.7 18.4
12.5
67.1
71.7
61.4
16.0
63.6
68.7
59.7
20.0
65.9
69.2
62.9
25.0
64.3
70.1
58.1
31.5
65.9
70.0
61.4
40.0
63.3
68.1
59.0
50.0
64.7
68.3
59.5
63.0
74.7
77.9
72.5
80.0
67.3
72.0
62.3
100
66.3
70.6
62.4
125
74.3
76.4
72.4
160
67.5
72.7
60.4
200
67.3
74.7
60.1
250
67.0
73.7
62.1
315
68.1
73.3
62.9
400
73.6
82.0
66.3
500
70.2
77.4
64.5
630
69.3
76.5
64.3
800 1000 1250 1600
71.6 72.3 73.6 72.8
84.2 80.4 81.9 83.9
63.4 64.9 63.2 60.4
2000
71.6
80.1
58.8
2500
68.1
77.0
56.1
3150
68.5
77.6
56.2
4000
66.6
76.0
53.2
5000
63.8
71.6
50.8
6300
61.0
70.6
47.6
8000100001250016000 20000
55.9 51.7 46.5 42.6 37.3
65.8 61.5 55.3 49.6 44.2
45.1 42.2 38.8 36.7 30.6
Summary
Filename
Serial Number
Model
Firmware Version
User
Location
Job Description
Note
Start
Stop
Duration
Run Time
Pause
Pre Calibration
Post Calibration
Overall Settings
RMS Weight
Peak Weight
Detector
Preamp
Integration Method
OBA Range
OBA Bandwidth
OBA Freq. Weighting
OBA Max Spectrum
Overload
Under Range Peak
Under Range Limit
Noise Floor
Results
LASeq
LASE
EAS
EAS8
EAS40
LZpeak (max)
LASmax
LASmin
SEA
LCSeq
LASeq
LCSeq - LASeq
LAIeq
LAeq
LAIeq - LAeq
# Overloads
Overload Duration
# OBA Overloads
Dose Settings
Dose Name
Exch. Rate
Threshold
Criterion Level
Criterion Duration
LxT_Data.075
2471
LxT1
1.522
RH
Air Intake
Roof top
2013/10/10 12:25:39
2013/10/10 12:26:25
0:00:46.4
0:00:46.4
0:00:00.0
2013/10/10 11:21:20
None
---
A Weighting
Z Weighting
Slow
PRMLxT1L
Exponential
Normal
1/3 Octave
Z Weighting
Bin Max
121.9 dB
A
77.0
26.0
16.2
72.1
88.8
84.242
52.288
261.439
2013/10/10 12:25:43
2013/10/10 12:25:39
2013/10/10 12:25:39
-99.9
dB
dB
µPa²h
mPa²h
mPa²h
103.0 dB
72.4 dB
71.1 dB
dB
0
0
0
0
0
89.4
72.1
17.3
72.6
72.1
0.4
0
0.0
0
0.0
C
Z
74.0 79.0 dB
25.2 32.0 dB
16.0 21.9 dB
0.0
0.0
0.0
0.0
0.0
s
s
s
s
s
dB
dB
dB
dB
dB
dB
s
s
OSHA 1
5
None
90
8
OSHA 2
5
80
90
8
dB
dB
dB
h
Results
Dose
Projected Dose
TWA (Projected)
TWA (t)
Lep (t)
0.0
8.4
72.1
25.7
44.2
-99.9
-99.9
-99.9
-99.9
44.2
%
%
dB
dB
dB
Statistics
LAS5.00
LAS10.00
LAS33.30
LAS50.00
LAS66.30
LAS90.00
72.3
72.3
72.2
72.1
72.1
72.0
dB
dB
dB
dB
dB
dB
Calibration History
Preamp
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
1/3 Octave
Frequency (Hz)
Overall 1/3 Spectra
Max 1/3 Spectra
Min 1/3 Spectra
2013/10/10
2013/08/15
2013/08/15
2013/07/25
2013/07/25
2013/07/11
2013/07/11
2013/06/28
2013/06/27
2013/06/27
2013/05/03
DatedB re. 1V/Pa
11:21:20
-27.9
12:57:41
-28.1
12:41:43
-27.9
15:00:18
-28.2
12:47:17
-27.9
14:00:51
-28.2
13:04:13
-27.9
11:57:52
-28.1
10:57:35
-28.1
10:57:11
-28.1
12:42:33
-29.2
6.3
66.5
71.7
61.1
8.0
65.1
70.8
58.2
10.0
62.0
67.8
53.0
6.3
65.1
70.3
69.4
79.0
67.4
78.1
65.8
46.5
43.9
41.9
8.0
62.4
67.7
71.2
71.8
56.4
66.1
79.0
55.9
51.1
47.0
10.0
54.3
72.8
58.0
53.9
58.2
62.2
70.5
63.3
54.6
55.5
12.5
64.9
72.5
69.3
53.0
65.4
69.9
68.2
61.4
61.4
61.3
16.0
51.5
72.0
63.2
64.6
60.1
70.1
63.6
59.2
61.1
57.5
20.0
55.0
68.5
66.4
69.6
65.6
72.9
63.9
50.6
54.9
58.0
25.0
61.1
68.7
71.8
61.8
64.7
62.2
59.5
54.4
53.0
46.5
31.5
68.4
74.5
69.9
61.2
62.9
69.6
62.5
50.9
48.5
60.1
40.0
76.5
64.5
80.9
57.2
64.1
56.8
53.8
54.0
46.1
56.3
50.0
72.5
62.2
66.4
50.7
63.5
54.3
55.8
49.1
59.2
52.8
63.0
68.4
66.7
70.2
50.6
65.9
63.4
57.7
48.4
49.4
62.7
80.0
71.4
58.4
74.3
43.5
67.9
61.3
62.4
45.8
46.9
62.2
100
58.9
59.2
65.0
59.9
62.9
63.4
61.1
50.9
41.7
48.6
125
65.3
61.1
61.2
61.6
71.4
54.8
62.6
49.4
43.0
50.0
160
62.5
61.4
63.0
34.4
75.1
63.9
58.3
46.3
44.2
50.4
200
54.9
56.8
62.7
56.4
68.5
60.2
61.5
46.5
42.9
48.4
250
55.6
59.5
59.6
57.3
67.6
62.3
70.1
45.7
39.3
47.9
315
54.9
55.9
56.0
46.9
66.8
60.3
72.8
38.5
36.7
52.3
400
51.7
55.7
59.0
42.9
66.4
57.7
66.2
33.9
34.0
37.7
500
50.1
48.2
59.4
40.4
67.0
49.8
49.9
34.3
27.8
42.2
630
44.0
39.6
52.1
28.4
58.2
39.6
45.3
30.3
19.3
43.5
800
30.2
32.9
46.8
19.9
45.3
32.9
33.5
28.3
11.8
29.4
1000
94.0
93.7
94.0
93.7
94.0
93.7
94.0
94.0
94.0
95.1
1250
28.9
28.9
31.0
28.4
32.3
28.8
29.4
29.2
29.1
30.0
1600
12.7
11.0
19.9
10.0
22.4
9.6
11.2
7.9
7.8
9.0
2000
35.4
34.6
35.2
35.5
35.3
35.6
35.6
35.3
34.8
36.0
2500
10.4
9.1
11.0
9.7
12.5
10.6
9.9
9.9
11.1
10.7
3150
43.5
43.2
43.7
43.1
43.6
43.2
43.4
43.2
43.4
44.5
4000
12.1
12.7
13.1
11.2
12.1
11.4
11.6
11.5
11.3
12.3
5000
15.6
14.7
16.5
14.3
15.3
16.6
14.9
15.0
15.5
16.0
6300
13.4
13.4
13.5
12.9
13.4
12.9
13.6
13.2
12.6
14.0
8000 10000 12500 16000 20000
14.4 15.2 16.6 17.4
14.7 15.3 16.7 17.5
14.6 16.1 16.6 17.7
14.3 15.3 16.2 17.6
15.1 16.1 16.7 17.7
14.4 15.8 16.4 17.2
14.5 15.1 16.1 17.8
14.7 15.6 16.7 17.3
14.5 15.1 16.4 17.6
15.5 16.3 17.7 18.4
12.5
68.0
70.5
64.3
16.0
67.4
71.3
62.6
20.0
73.2
76.4
70.0
25.0
78.3
81.8
71.9
31.5
79.2
82.0
75.9
40.0
88.0
91.7
84.5
50.0
85.7
88.2
82.9
63.0
79.2
82.2
63.5
80.0
71.7
74.8
68.2
100
68.6
70.3
66.0
125
71.8
73.9
69.3
160
68.8
70.1
66.8
200
66.4
70.4
64.5
250
64.1
66.0
62.7
315
61.7
62.7
59.6
400
66.7
68.6
62.3
500
64.7
65.5
62.5
630
61.5
62.4
57.9
800 1000 1250 1600
60.4 62.3 61.5 61.6
64.5 63.7 62.3 62.5
59.6 61.5 57.6 61.1
2000
61.2
62.3
60.6
2500
58.2
61.2
57.5
3150
56.2
56.7
55.8
4000
52.3
53.2
50.9
5000
51.3
52.0
50.5
6300
53.1
55.2
51.4
8000100001250016000 20000
49.8 42.7 38.3 33.3 26.9
50.8 43.8 39.0 34.5 29.2
49.0 42.0 35.3 31.2 26.0
Summary
Filename
Serial Number
Model
Firmware Version
User
Location
Job Description
Note
Start
Stop
Duration
Run Time
Pause
Pre Calibration
Post Calibration
Overall Settings
RMS Weight
Peak Weight
Detector
Preamp
Integration Method
OBA Range
OBA Bandwidth
OBA Freq. Weighting
OBA Max Spectrum
Overload
Under Range Peak
Under Range Limit
Noise Floor
Results
LASeq
LASE
EAS
EAS8
EAS40
LZpeak (max)
LASmax
LASmin
SEA
LCSeq
LASeq
LCSeq - LASeq
LAIeq
LAeq
LAIeq - LAeq
# Overloads
Overload Duration
# OBA Overloads
Dose Settings
Dose Name
Exch. Rate
Threshold
Criterion Level
Criterion Duration
LxT_Data.076
2471
LxT1
1.522
RH
ES4 ES5
Roof top
2013/10/10 12:27:08
2013/10/10 12:27:53
0:00:45.9
0:00:45.9
0:00:00.0
2013/10/10 11:21:20
None
---
A Weighting
Z Weighting
Slow
PRMLxT1L
Exponential
Normal
1/3 Octave
Z Weighting
Bin Max
121.9 dB
A
77.0
26.0
16.2
67.6
84.2
29.107
18.263
91.315
2013/10/10 12:27:08
2013/10/10 12:27:41
2013/10/10 12:27:26
-99.9
dB
dB
µPa²h
mPa²h
mPa²h
103.7 dB
68.1 dB
66.9 dB
dB
0
0
0
0
0
89.2
67.6
21.6
68.5
67.6
0.9
0
0.0
0
0.0
C
Z
74.0 79.0 dB
25.2 32.0 dB
16.0 21.9 dB
0.0
0.0
0.0
0.0
0.0
s
s
s
s
s
dB
dB
dB
dB
dB
dB
s
s
OSHA 1
5
None
90
8
OSHA 2
5
80
90
8
dB
dB
dB
h
Results
Dose
Projected Dose
TWA (Projected)
TWA (t)
Lep (t)
0.0
4.5
67.6
21.1
39.6
-99.9
-99.9
-99.9
-99.9
39.6
%
%
dB
dB
dB
Statistics
LAS5.00
LAS10.00
LAS33.30
LAS50.00
LAS66.30
LAS90.00
67.9
67.9
67.7
67.6
67.5
67.2
dB
dB
dB
dB
dB
dB
Calibration History
Preamp
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
1/3 Octave
Frequency (Hz)
Overall 1/3 Spectra
Max 1/3 Spectra
Min 1/3 Spectra
2013/10/10
2013/08/15
2013/08/15
2013/07/25
2013/07/25
2013/07/11
2013/07/11
2013/06/28
2013/06/27
2013/06/27
2013/05/03
Date dB re. 1V/Pa
11:21:20
-27.9
12:57:41
-28.1
12:41:43
-27.9
15:00:18
-28.2
12:47:17
-27.9
14:00:51
-28.2
13:04:13
-27.9
11:57:52
-28.1
10:57:35
-28.1
10:57:11
-28.1
12:42:33
-29.2
6.3
67.1
71.3
61.4
8.0
65.2
70.1
53.8
10.0
62.9
65.4
56.6
6.3
65.1
70.3
69.4
79.0
67.4
78.1
65.8
46.5
43.9
41.9
8.0
62.4
67.7
71.2
71.8
56.4
66.1
79.0
55.9
51.1
47.0
10.0
54.3
72.8
58.0
53.9
58.2
62.2
70.5
63.3
54.6
55.5
12.5
64.9
72.5
69.3
53.0
65.4
69.9
68.2
61.4
61.4
61.3
16.0
51.5
72.0
63.2
64.6
60.1
70.1
63.6
59.2
61.1
57.5
20.0
55.0
68.5
66.4
69.6
65.6
72.9
63.9
50.6
54.9
58.0
25.0
61.1
68.7
71.8
61.8
64.7
62.2
59.5
54.4
53.0
46.5
31.5
68.4
74.5
69.9
61.2
62.9
69.6
62.5
50.9
48.5
60.1
40.0
76.5
64.5
80.9
57.2
64.1
56.8
53.8
54.0
46.1
56.3
50.0
72.5
62.2
66.4
50.7
63.5
54.3
55.8
49.1
59.2
52.8
63.0
68.4
66.7
70.2
50.6
65.9
63.4
57.7
48.4
49.4
62.7
80.0
71.4
58.4
74.3
43.5
67.9
61.3
62.4
45.8
46.9
62.2
100
58.9
59.2
65.0
59.9
62.9
63.4
61.1
50.9
41.7
48.6
125
65.3
61.1
61.2
61.6
71.4
54.8
62.6
49.4
43.0
50.0
160
62.5
61.4
63.0
34.4
75.1
63.9
58.3
46.3
44.2
50.4
200
54.9
56.8
62.7
56.4
68.5
60.2
61.5
46.5
42.9
48.4
250
55.6
59.5
59.6
57.3
67.6
62.3
70.1
45.7
39.3
47.9
315
54.9
55.9
56.0
46.9
66.8
60.3
72.8
38.5
36.7
52.3
400
51.7
55.7
59.0
42.9
66.4
57.7
66.2
33.9
34.0
37.7
500
50.1
48.2
59.4
40.4
67.0
49.8
49.9
34.3
27.8
42.2
630
44.0
39.6
52.1
28.4
58.2
39.6
45.3
30.3
19.3
43.5
800
30.2
32.9
46.8
19.9
45.3
32.9
33.5
28.3
11.8
29.4
1000
94.0
93.7
94.0
93.7
94.0
93.7
94.0
94.0
94.0
95.1
1250
28.9
28.9
31.0
28.4
32.3
28.8
29.4
29.2
29.1
30.0
1600
12.7
11.0
19.9
10.0
22.4
9.6
11.2
7.9
7.8
9.0
2000
35.4
34.6
35.2
35.5
35.3
35.6
35.6
35.3
34.8
36.0
2500
10.4
9.1
11.0
9.7
12.5
10.6
9.9
9.9
11.1
10.7
3150
43.5
43.2
43.7
43.1
43.6
43.2
43.4
43.2
43.4
44.5
4000
12.1
12.7
13.1
11.2
12.1
11.4
11.6
11.5
11.3
12.3
5000
15.6
14.7
16.5
14.3
15.3
16.6
14.9
15.0
15.5
16.0
6300
13.4
13.4
13.5
12.9
13.4
12.9
13.6
13.2
12.6
14.0
8000 10000 12500 16000 20000
14.4 15.2 16.6 17.4
14.7 15.3 16.7 17.5
14.6 16.1 16.6 17.7
14.3 15.3 16.2 17.6
15.1 16.1 16.7 17.7
14.4 15.8 16.4 17.2
14.5 15.1 16.1 17.8
14.7 15.6 16.7 17.3
14.5 15.1 16.4 17.6
15.5 16.3 17.7 18.4
12.5
67.5
71.1
62.5
16.0
67.9
70.7
64.1
20.0
74.8
77.7
70.7
25.0
80.8
87.6
77.6
31.5
79.7
82.3
75.5
40.0
89.0
90.8
84.4
50.0
82.5
84.5
80.3
63.0
75.2
77.3
72.7
80.0
71.2
73.0
58.7
100
71.7
73.1
68.8
125
74.2
77.8
72.1
160
72.3
76.0
70.6
200
66.8
68.9
63.5
250
64.6
66.7
54.1
315
61.9
66.0
59.6
400
57.9
62.2
56.0
500
58.5
59.5
57.6
630
56.8
57.9
52.2
800 1000 1250 1600
56.9 56.0 52.6 52.8
59.9 57.6 53.3 57.3
55.4 54.9 49.0 52.0
2000
51.1
53.1
50.2
2500
48.9
49.9
48.0
3150
47.5
48.2
41.7
4000
44.1
45.4
43.3
5000
41.3
42.1
40.0
6300
40.7
42.3
39.1
8000100001250016000 20000
37.9 33.6 27.5 24.2 21.8
38.6 34.8 29.5 25.5 30.9
37.0 32.6 26.5 23.1 20.5
Summary
Filename
Serial Number
Model
Firmware Version
User
Location
Job Description
Note
Start
Stop
Duration
Run Time
Pause
Pre Calibration
Post Calibration
Overall Settings
RMS Weight
Peak Weight
Detector
Preamp
Integration Method
OBA Range
OBA Bandwidth
OBA Freq. Weighting
OBA Max Spectrum
Overload
Under Range Peak
Under Range Limit
Noise Floor
Results
LASeq
LASE
EAS
EAS8
EAS40
LZpeak (max)
LASmax
LASmin
SEA
LCSeq
LASeq
LCSeq - LASeq
LAIeq
LAeq
LAIeq - LAeq
# Overloads
Overload Duration
# OBA Overloads
Dose Settings
Dose Name
Exch. Rate
Threshold
Criterion Level
Criterion Duration
LxT_Data.077
2471
LxT1
1.522
RH
CU5, CU6, CU7
Roof top
2013/10/10 12:30:42
2013/10/10 12:31:31
0:00:48.9
0:00:48.9
0:00:00.0
2013/10/10 11:21:20
None
---
A Weighting
Z Weighting
Slow
PRMLxT1L
Exponential
Normal
1/3 Octave
Z Weighting
Bin Max
121.9 dB
A
77.0
26.0
16.2
74.5
91.4
152.302
89.699
448.495
2013/10/10 12:31:00
2013/10/10 12:30:57
2013/10/10 12:30:42
-99.9
dB
dB
µPa²h
mPa²h
mPa²h
97.6 dB
75.1 dB
72.2 dB
dB
0
0
0
0
0
81.7
74.5
7.2
75.5
74.5
1.0
0
0.0
0
0.0
C
Z
74.0 79.0 dB
25.2 32.0 dB
16.0 21.9 dB
0.0
0.0
0.0
0.0
0.0
s
s
s
s
s
dB
dB
dB
dB
dB
dB
s
s
OSHA 1
5
None
90
8
OSHA 2
5
80
90
8
dB
dB
dB
h
Results
Dose
Projected Dose
TWA (Projected)
TWA (t)
Lep (t)
0.0
11.6
74.5
28.5
46.8
-99.9
-99.9
-99.9
-99.9
46.8
%
%
dB
dB
dB
Statistics
LAS5.00
LAS10.00
LAS33.30
LAS50.00
LAS66.30
LAS90.00
74.9
74.9
74.6
74.5
74.4
73.9
dB
dB
dB
dB
dB
dB
Calibration History
Preamp
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
1/3 Octave
Frequency (Hz)
Overall 1/3 Spectra
Max 1/3 Spectra
Min 1/3 Spectra
2013/10/10
2013/08/15
2013/08/15
2013/07/25
2013/07/25
2013/07/11
2013/07/11
2013/06/28
2013/06/27
2013/06/27
2013/05/03
DatedB re. 1V/Pa
11:21:20
-27.9
12:57:41
-28.1
12:41:43
-27.9
15:00:18
-28.2
12:47:17
-27.9
14:00:51
-28.2
13:04:13
-27.9
11:57:52
-28.1
10:57:35
-28.1
10:57:11
-28.1
12:42:33
-29.2
6.3
60.8
67.6
52.3
8.0
63.5
69.8
56.0
10.0
60.7
66.5
55.3
6.3
65.1
70.3
69.4
79.0
67.4
78.1
65.8
46.5
43.9
41.9
8.0
62.4
67.7
71.2
71.8
56.4
66.1
79.0
55.9
51.1
47.0
10.0
54.3
72.8
58.0
53.9
58.2
62.2
70.5
63.3
54.6
55.5
12.5
64.9
72.5
69.3
53.0
65.4
69.9
68.2
61.4
61.4
61.3
16.0
51.5
72.0
63.2
64.6
60.1
70.1
63.6
59.2
61.1
57.5
20.0
55.0
68.5
66.4
69.6
65.6
72.9
63.9
50.6
54.9
58.0
25.0
61.1
68.7
71.8
61.8
64.7
62.2
59.5
54.4
53.0
46.5
31.5
68.4
74.5
69.9
61.2
62.9
69.6
62.5
50.9
48.5
60.1
40.0
76.5
64.5
80.9
57.2
64.1
56.8
53.8
54.0
46.1
56.3
50.0
72.5
62.2
66.4
50.7
63.5
54.3
55.8
49.1
59.2
52.8
63.0
68.4
66.7
70.2
50.6
65.9
63.4
57.7
48.4
49.4
62.7
80.0
71.4
58.4
74.3
43.5
67.9
61.3
62.4
45.8
46.9
62.2
100
58.9
59.2
65.0
59.9
62.9
63.4
61.1
50.9
41.7
48.6
125
65.3
61.1
61.2
61.6
71.4
54.8
62.6
49.4
43.0
50.0
160
62.5
61.4
63.0
34.4
75.1
63.9
58.3
46.3
44.2
50.4
200
54.9
56.8
62.7
56.4
68.5
60.2
61.5
46.5
42.9
48.4
250
55.6
59.5
59.6
57.3
67.6
62.3
70.1
45.7
39.3
47.9
315
54.9
55.9
56.0
46.9
66.8
60.3
72.8
38.5
36.7
52.3
400
51.7
55.7
59.0
42.9
66.4
57.7
66.2
33.9
34.0
37.7
500
50.1
48.2
59.4
40.4
67.0
49.8
49.9
34.3
27.8
42.2
630
44.0
39.6
52.1
28.4
58.2
39.6
45.3
30.3
19.3
43.5
800
30.2
32.9
46.8
19.9
45.3
32.9
33.5
28.3
11.8
29.4
1000
94.0
93.7
94.0
93.7
94.0
93.7
94.0
94.0
94.0
95.1
1250
28.9
28.9
31.0
28.4
32.3
28.8
29.4
29.2
29.1
30.0
1600
12.7
11.0
19.9
10.0
22.4
9.6
11.2
7.9
7.8
9.0
2000
35.4
34.6
35.2
35.5
35.3
35.6
35.6
35.3
34.8
36.0
2500
10.4
9.1
11.0
9.7
12.5
10.6
9.9
9.9
11.1
10.7
3150
43.5
43.2
43.7
43.1
43.6
43.2
43.4
43.2
43.4
44.5
4000
12.1
12.7
13.1
11.2
12.1
11.4
11.6
11.5
11.3
12.3
5000
15.6
14.7
16.5
14.3
15.3
16.6
14.9
15.0
15.5
16.0
6300
13.4
13.4
13.5
12.9
13.4
12.9
13.6
13.2
12.6
14.0
8000 10000 12500 16000 20000
14.4 15.2 16.6 17.4
14.7 15.3 16.7 17.5
14.6 16.1 16.6 17.7
14.3 15.3 16.2 17.6
15.1 16.1 16.7 17.7
14.4 15.8 16.4 17.2
14.5 15.1 16.1 17.8
14.7 15.6 16.7 17.3
14.5 15.1 16.4 17.6
15.5 16.3 17.7 18.4
12.5
64.5
67.7
57.7
16.0
68.9
72.1
64.9
20.0
66.4
69.1
62.4
25.0
62.8
66.0
59.9
31.5
66.1
70.0
61.1
40.0
69.9
73.8
66.1
50.0
70.3
73.0
67.0
63.0
71.8
75.4
64.2
80.0
71.6
73.5
64.5
100
68.1
69.8
65.6
125
71.1
73.3
66.8
160
70.2
71.5
68.7
200
65.8
68.6
63.9
250
67.6
69.1
64.9
315
74.6
75.5
68.9
400
73.2
74.3
66.5
500
63.5
66.9
62.6
630
64.7
65.7
61.9
800 1000 1250 1600
66.4 62.6 60.4 58.6
68.1 64.1 61.7 59.8
63.7 59.9 59.7 56.4
2000
57.6
59.4
57.1
2500
56.0
58.4
53.6
3150
54.7
59.2
53.3
4000
55.1
59.7
53.5
5000
51.0
55.9
49.9
6300
49.5
55.0
48.6
8000100001250016000 20000
50.0 49.8 44.1 40.5 34.9
55.1 53.1 48.7 43.4 37.3
49.0 48.9 42.5 38.5 32.5
Summary
Filename
Serial Number
Model
Firmware Version
User
Location
Job Description
Note
Start
Stop
Duration
Run Time
Pause
Pre Calibration
Post Calibration
Overall Settings
RMS Weight
Peak Weight
Detector
Preamp
Integration Method
OBA Range
OBA Bandwidth
OBA Freq. Weighting
OBA Max Spectrum
Overload
Under Range Peak
Under Range Limit
Noise Floor
Results
LASeq
LASE
EAS
EAS8
EAS40
LZpeak (max)
LASmax
LASmin
SEA
LCSeq
LASeq
LCSeq - LASeq
LAIeq
LAeq
LAIeq - LAeq
# Overloads
Overload Duration
# OBA Overloads
Dose Settings
Dose Name
Exch. Rate
Threshold
Criterion Level
Criterion Duration
LxT_Data.078
2471
LxT1
1.522
RH
CU11
Roof top
2013/10/10 12:33:55
2013/10/10 12:34:46
0:00:51.0
0:00:51.0
0:00:00.0
2013/10/10 11:21:20
None
---
A Weighting
Z Weighting
Slow
PRMLxT1L
Exponential
Normal
1/3 Octave
Z Weighting
Bin Max
121.9 dB
A
77.0
26.0
16.2
73.8
90.8
134.705
76.069
380.343
2013/10/10 12:33:55
2013/10/10 12:34:38
2013/10/10 12:33:55
-99.9
dB
dB
µPa²h
mPa²h
mPa²h
97.9 dB
74.2 dB
72.0 dB
dB
0
0
0
0
0
82.0
73.8
8.2
74.2
73.8
0.5
0
0.0
0
0.0
C
Z
74.0 79.0 dB
25.2 32.0 dB
16.0 21.9 dB
0.0
0.0
0.0
0.0
0.0
s
s
s
s
s
dB
dB
dB
dB
dB
dB
s
s
OSHA 1 OSHA 2
5
5 dB
None
80 dB
90
90 dB
8
8 h
Results
Dose
Projected Dose
TWA (Projected)
TWA (t)
Lep (t)
0.0
10.5
73.8
28.1
46.2
Statistics
LAS5.00
LAS10.00
LAS33.30
LAS50.00
LAS66.30
LAS90.00
74.1
74.0
73.8
73.8
73.7
73.6
-99.9
-99.9
-99.9
-99.9
46.2
dB
dB
dB
dB
dB
dB
%
%
dB
dB
dB
Calibration History
Preamp
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
1/3 Octave
Frequency (Hz)
Overall 1/3 Spectra
Max 1/3 Spectra
Min 1/3 Spectra
2013/10/10
2013/08/15
2013/08/15
2013/07/25
2013/07/25
2013/07/11
2013/07/11
2013/06/28
2013/06/27
2013/06/27
2013/05/03
Date
dB re. 1V/Pa
11:21:20
-27.9
12:57:41
-28.1
12:41:43
-27.9
15:00:18
-28.2
12:47:17
-27.9
14:00:51
-28.2
13:04:13
-27.9
11:57:52
-28.1
10:57:35
-28.1
10:57:11
-28.1
12:42:33
-29.2
6.3
61.5
67.6
55.2
8.0
61.4
66.4
54.9
10.0
60.6
67.7
53.6
6.3
65.1
70.3
69.4
79.0
67.4
78.1
65.8
46.5
43.9
41.9
8.0
62.4
67.7
71.2
71.8
56.4
66.1
79.0
55.9
51.1
47.0
10.0
54.3
72.8
58.0
53.9
58.2
62.2
70.5
63.3
54.6
55.5
12.5
64.9
72.5
69.3
53.0
65.4
69.9
68.2
61.4
61.4
61.3
16.0
51.5
72.0
63.2
64.6
60.1
70.1
63.6
59.2
61.1
57.5
20.0
55.0
68.5
66.4
69.6
65.6
72.9
63.9
50.6
54.9
58.0
25.0
61.1
68.7
71.8
61.8
64.7
62.2
59.5
54.4
53.0
46.5
31.5
68.4
74.5
69.9
61.2
62.9
69.6
62.5
50.9
48.5
60.1
40.0
76.5
64.5
80.9
57.2
64.1
56.8
53.8
54.0
46.1
56.3
50.0
72.5
62.2
66.4
50.7
63.5
54.3
55.8
49.1
59.2
52.8
63.0
68.4
66.7
70.2
50.6
65.9
63.4
57.7
48.4
49.4
62.7
80.0
71.4
58.4
74.3
43.5
67.9
61.3
62.4
45.8
46.9
62.2
100
58.9
59.2
65.0
59.9
62.9
63.4
61.1
50.9
41.7
48.6
125
65.3
61.1
61.2
61.6
71.4
54.8
62.6
49.4
43.0
50.0
160
62.5
61.4
63.0
34.4
75.1
63.9
58.3
46.3
44.2
50.4
200
54.9
56.8
62.7
56.4
68.5
60.2
61.5
46.5
42.9
48.4
250
55.6
59.5
59.6
57.3
67.6
62.3
70.1
45.7
39.3
47.9
315
54.9
55.9
56.0
46.9
66.8
60.3
72.8
38.5
36.7
52.3
400
51.7
55.7
59.0
42.9
66.4
57.7
66.2
33.9
34.0
37.7
500
50.1
48.2
59.4
40.4
67.0
49.8
49.9
34.3
27.8
42.2
630
44.0
39.6
52.1
28.4
58.2
39.6
45.3
30.3
19.3
43.5
800
30.2
32.9
46.8
19.9
45.3
32.9
33.5
28.3
11.8
29.4
1000
94.0
93.7
94.0
93.7
94.0
93.7
94.0
94.0
94.0
95.1
1250
28.9
28.9
31.0
28.4
32.3
28.8
29.4
29.2
29.1
30.0
1600
12.7
11.0
19.9
10.0
22.4
9.6
11.2
7.9
7.8
9.0
2000
35.4
34.6
35.2
35.5
35.3
35.6
35.6
35.3
34.8
36.0
2500
10.4
9.1
11.0
9.7
12.5
10.6
9.9
9.9
11.1
10.7
3150
43.5
43.2
43.7
43.1
43.6
43.2
43.4
43.2
43.4
44.5
4000
12.1
12.7
13.1
11.2
12.1
11.4
11.6
11.5
11.3
12.3
5000
15.6
14.7
16.5
14.3
15.3
16.6
14.9
15.0
15.5
16.0
6300
13.4
13.4
13.5
12.9
13.4
12.9
13.6
13.2
12.6
14.0
8000 10000 12500 16000 20000
14.4 15.2 16.6 17.4
14.7 15.3 16.7 17.5
14.6 16.1 16.6 17.7
14.3 15.3 16.2 17.6
15.1 16.1 16.7 17.7
14.4 15.8 16.4 17.2
14.5 15.1 16.1 17.8
14.7 15.6 16.7 17.3
14.5 15.1 16.4 17.6
15.5 16.3 17.7 18.4
12.5
64.3
72.5
59.5
16.0
62.2
65.5
50.8
20.0
62.6
66.1
57.3
25.0
62.9
65.1
55.3
31.5
63.9
67.4
46.7
40.0
66.6
72.2
61.8
50.0
71.8
74.7
66.4
63.0
70.3
73.6
64.7
80.0
66.4
69.8
64.3
100
74.8
77.0
61.4
125
73.9
75.5
72.2
160
67.9
71.2
66.6
200
68.0
69.5
63.8
250
74.8
76.2
72.8
315
67.7
69.1
66.3
400
70.1
72.8
64.9
500
65.8
67.0
64.1
630
64.0
66.3
62.5
800
63.8
64.5
62.7
1000
64.2
65.3
63.0
1250
60.4
61.5
58.4
1600
63.0
66.3
57.5
2000
57.2
57.9
56.5
2500
55.4
56.1
52.7
3150
54.8
56.2
53.0
4000
51.6
53.4
49.2
5000
50.3
52.0
48.7
6300
49.4
50.9
46.6
8000100001250016000 20000
49.8 46.2 43.0 41.2 35.5
51.5 47.4 44.4 42.5 37.1
49.0 44.9 40.4 39.0 32.5
Summary
Filename
Serial Number
Model
Firmware Version
User
Location
Job Description
Note
Start
Stop
Duration
Run Time
Pause
Pre Calibration
Post Calibration
Overall Settings
RMS Weight
Peak Weight
Detector
Preamp
Integration Method
OBA Range
OBA Bandwidth
OBA Freq. Weighting
OBA Max Spectrum
Overload
Under Range Peak
Under Range Limit
Noise Floor
Results
LASeq
LASE
EAS
EAS8
EAS40
LZpeak (max)
LASmax
LASmin
SEA
LCSeq
LASeq
LCSeq - LASeq
LAIeq
LAeq
LAIeq - LAeq
# Overloads
Overload Duration
# OBA Overloads
Dose Settings
Dose Name
Exch. Rate
Threshold
Criterion Level
Criterion Duration
LxT_Data.079
2471
LxT1
1.522
RH
CU12 and CU13
Roof top
2013/10/10 12:36:47
2013/10/10 12:37:33
0:00:45.7
0:00:45.7
0:00:00.0
2013/10/10 11:21:20
None
---
A Weighting
Z Weighting
Slow
PRMLxT1L
Exponential
Normal
1/3 Octave
Z Weighting
Bin Max
121.9 dB
A
77.0
26.0
16.2
70.1
86.7
51.807
32.649
163.243
2013/10/10 12:36:48
2013/10/10 12:36:48
2013/10/10 12:37:01
-99.9
dB
dB
µPa²h
mPa²h
mPa²h
98.6 dB
70.5 dB
69.7 dB
dB
0
0
0
0
0
78.8
70.1
8.8
70.5
70.1
0.4
0
0.0
0
0.0
C
Z
74.0 79.0 dB
25.2 32.0 dB
16.0 21.9 dB
0.0
0.0
0.0
0.0
0.0
s
s
s
s
s
dB
dB
dB
dB
dB
dB
s
s
OSHA 1
5
None
90
8
OSHA 2
5
80
90
8
dB
dB
dB
h
Results
Dose
Projected Dose
TWA (Projected)
TWA (t)
Lep (t)
0.0
6.3
70.1
23.6
42.1
-99.9
-99.9
-99.9
-99.9
42.1
%
%
dB
dB
dB
Statistics
LAS5.00
LAS10.00
LAS33.30
LAS50.00
LAS66.30
LAS90.00
70.3
70.3
70.1
70.1
70.0
69.9
dB
dB
dB
dB
dB
dB
Calibration History
Preamp
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
1/3 Octave
Frequency (Hz)
Overall 1/3 Spectra
Max 1/3 Spectra
Min 1/3 Spectra
2013/10/10
2013/08/15
2013/08/15
2013/07/25
2013/07/25
2013/07/11
2013/07/11
2013/06/28
2013/06/27
2013/06/27
2013/05/03
Date
dB re. 1V/Pa
11:21:20
-27.9
12:57:41
-28.1
12:41:43
-27.9
15:00:18
-28.2
12:47:17
-27.9
14:00:51
-28.2
13:04:13
-27.9
11:57:52
-28.1
10:57:35
-28.1
10:57:11
-28.1
12:42:33
-29.2
6.3
63.4
71.1
53.5
8.0
62.4
70.1
52.5
10.0
57.6
63.8
52.1
6.3
65.1
70.3
69.4
79.0
67.4
78.1
65.8
46.5
43.9
41.9
8.0
62.4
67.7
71.2
71.8
56.4
66.1
79.0
55.9
51.1
47.0
10.0
54.3
72.8
58.0
53.9
58.2
62.2
70.5
63.3
54.6
55.5
12.5
64.9
72.5
69.3
53.0
65.4
69.9
68.2
61.4
61.4
61.3
16.0
51.5
72.0
63.2
64.6
60.1
70.1
63.6
59.2
61.1
57.5
20.0
55.0
68.5
66.4
69.6
65.6
72.9
63.9
50.6
54.9
58.0
25.0
61.1
68.7
71.8
61.8
64.7
62.2
59.5
54.4
53.0
46.5
31.5
68.4
74.5
69.9
61.2
62.9
69.6
62.5
50.9
48.5
60.1
40.0
76.5
64.5
80.9
57.2
64.1
56.8
53.8
54.0
46.1
56.3
50.0
72.5
62.2
66.4
50.7
63.5
54.3
55.8
49.1
59.2
52.8
63.0
68.4
66.7
70.2
50.6
65.9
63.4
57.7
48.4
49.4
62.7
80.0
71.4
58.4
74.3
43.5
67.9
61.3
62.4
45.8
46.9
62.2
100
58.9
59.2
65.0
59.9
62.9
63.4
61.1
50.9
41.7
48.6
125
65.3
61.1
61.2
61.6
71.4
54.8
62.6
49.4
43.0
50.0
160
62.5
61.4
63.0
34.4
75.1
63.9
58.3
46.3
44.2
50.4
200
54.9
56.8
62.7
56.4
68.5
60.2
61.5
46.5
42.9
48.4
250
55.6
59.5
59.6
57.3
67.6
62.3
70.1
45.7
39.3
47.9
315
54.9
55.9
56.0
46.9
66.8
60.3
72.8
38.5
36.7
52.3
400
51.7
55.7
59.0
42.9
66.4
57.7
66.2
33.9
34.0
37.7
500
50.1
48.2
59.4
40.4
67.0
49.8
49.9
34.3
27.8
42.2
630
44.0
39.6
52.1
28.4
58.2
39.6
45.3
30.3
19.3
43.5
800
30.2
32.9
46.8
19.9
45.3
32.9
33.5
28.3
11.8
29.4
1000
94.0
93.7
94.0
93.7
94.0
93.7
94.0
94.0
94.0
95.1
1250
28.9
28.9
31.0
28.4
32.3
28.8
29.4
29.2
29.1
30.0
1600
12.7
11.0
19.9
10.0
22.4
9.6
11.2
7.9
7.8
9.0
2000
35.4
34.6
35.2
35.5
35.3
35.6
35.6
35.3
34.8
36.0
2500
10.4
9.1
11.0
9.7
12.5
10.6
9.9
9.9
11.1
10.7
3150
43.5
43.2
43.7
43.1
43.6
43.2
43.4
43.2
43.4
44.5
4000
12.1
12.7
13.1
11.2
12.1
11.4
11.6
11.5
11.3
12.3
5000
15.6
14.7
16.5
14.3
15.3
16.6
14.9
15.0
15.5
16.0
6300
13.4
13.4
13.5
12.9
13.4
12.9
13.6
13.2
12.6
14.0
8000 10000 12500 16000 20000
14.4 15.2 16.6 17.4
14.7 15.3 16.7 17.5
14.6 16.1 16.6 17.7
14.3 15.3 16.2 17.6
15.1 16.1 16.7 17.7
14.4 15.8 16.4 17.2
14.5 15.1 16.1 17.8
14.7 15.6 16.7 17.3
14.5 15.1 16.4 17.6
15.5 16.3 17.7 18.4
12.5
58.3
64.6
52.4
16.0
58.0
64.7
53.9
20.0
68.2
71.5
63.7
25.0
60.1
63.3
55.8
31.5
59.7
62.1
57.3
40.0
69.4
72.7
67.0
50.0
71.1
72.9
68.4
63.0
67.8
71.1
64.1
80.0
67.9
71.5
63.9
100
69.2
71.0
66.4
125
67.3
70.9
65.1
160
71.9
74.5
67.6
200
65.1
66.3
62.0
250
66.6
67.8
62.5
315
65.7
66.9
60.6
400
63.4
66.5
62.0
500
60.2
62.9
59.0
630
60.6
61.7
59.6
800
60.4
61.1
59.6
1000
61.0
62.6
60.2
1250
58.9
59.5
57.1
1600
57.2
57.8
54.3
2000
56.1
56.7
55.5
2500
55.0
56.1
54.2
3150
54.6
55.1
53.9
4000
53.6
54.2
51.6
5000
52.4
53.0
51.5
6300
48.7
49.3
47.7
8000100001250016000 20000
44.3 39.8 35.8 32.2 28.0
45.2 43.2 40.9 38.1 35.0
43.1 38.7 33.4 30.0 26.2
Summary
Filename
Serial Number
Model
Firmware Version
User
Location
Job Description
Note
Start
Stop
Duration
Run Time
Pause
Pre Calibration
Post Calibration
Overall Settings
RMS Weight
Peak Weight
Detector
Preamp
Integration Method
OBA Range
OBA Bandwidth
OBA Freq. Weighting
OBA Max Spectrum
Overload
Under Range Peak
Under Range Limit
Noise Floor
Results
LASeq
LASE
EAS
EAS8
EAS40
LZpeak (max)
LASmax
LASmin
SEA
LCSeq
LASeq
LCSeq - LASeq
LAIeq
LAeq
LAIeq - LAeq
# Overloads
Overload Duration
# OBA Overloads
Dose Settings
Dose Name
Exch. Rate
Threshold
Criterion Level
Criterion Duration
LxT_Data.080
2471
LxT1
1.522
RH
CU18 and CU19
Roof top
2013/10/10 12:40:29
2013/10/10 12:41:12
0:00:42.7
0:00:42.7
0:00:00.0
2013/10/10 11:21:20
None
---
A Weighting
Z Weighting
Slow
PRMLxT1L
Exponential
Normal
1/3 Octave
Z Weighting
Bin Max
121.9 dB
A
77.0
26.0
16.2
73.0
89.3
95.254
64.246
321.231
2013/10/10 12:40:58
2013/10/10 12:40:29
2013/10/10 12:40:35
-99.9
dB
dB
µPa²h
mPa²h
mPa²h
94.9 dB
74.0 dB
72.7 dB
dB
0
0
0
0
0
80.9
73.0
7.8
73.4
73.0
0.4
0
0.0
0
0.0
C
Z
74.0 79.0 dB
25.2 32.0 dB
16.0 21.9 dB
0.0
0.0
0.0
0.0
0.0
s
s
s
s
s
dB
dB
dB
dB
dB
dB
s
s
OSHA 1
5
None
90
8
OSHA 2
5
80
90
8
dB
dB
dB
h
Results
Dose
Projected Dose
TWA (Projected)
TWA (t)
Lep (t)
0.0
9.5
73.0
26.0
44.7
-99.9
-99.9
-99.9
-99.9
44.7
%
%
dB
dB
dB
Statistics
LAS5.00
LAS10.00
LAS33.30
LAS50.00
LAS66.30
LAS90.00
73.3
73.2
73.1
73.0
72.9
72.8
dB
dB
dB
dB
dB
dB
Calibration History
Preamp
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
1/3 Octave
Frequency (Hz)
Overall 1/3 Spectra
Max 1/3 Spectra
Min 1/3 Spectra
2013/10/10
2013/08/15
2013/08/15
2013/07/25
2013/07/25
2013/07/11
2013/07/11
2013/06/28
2013/06/27
2013/06/27
2013/05/03
DatedB re. 1V/Pa
11:21:20
-27.9
12:57:41
-28.1
12:41:43
-27.9
15:00:18
-28.2
12:47:17
-27.9
14:00:51
-28.2
13:04:13
-27.9
11:57:52
-28.1
10:57:35
-28.1
10:57:11
-28.1
12:42:33
-29.2
6.3
72.9
87.1
53.7
8.0
63.6
73.4
56.5
10.0
61.4
66.6
55.7
6.3
65.1
70.3
69.4
79.0
67.4
78.1
65.8
46.5
43.9
41.9
8.0
62.4
67.7
71.2
71.8
56.4
66.1
79.0
55.9
51.1
47.0
10.0
54.3
72.8
58.0
53.9
58.2
62.2
70.5
63.3
54.6
55.5
12.5
64.9
72.5
69.3
53.0
65.4
69.9
68.2
61.4
61.4
61.3
16.0
51.5
72.0
63.2
64.6
60.1
70.1
63.6
59.2
61.1
57.5
20.0
55.0
68.5
66.4
69.6
65.6
72.9
63.9
50.6
54.9
58.0
25.0
61.1
68.7
71.8
61.8
64.7
62.2
59.5
54.4
53.0
46.5
31.5
68.4
74.5
69.9
61.2
62.9
69.6
62.5
50.9
48.5
60.1
40.0
76.5
64.5
80.9
57.2
64.1
56.8
53.8
54.0
46.1
56.3
50.0
72.5
62.2
66.4
50.7
63.5
54.3
55.8
49.1
59.2
52.8
63.0
68.4
66.7
70.2
50.6
65.9
63.4
57.7
48.4
49.4
62.7
80.0
71.4
58.4
74.3
43.5
67.9
61.3
62.4
45.8
46.9
62.2
100
58.9
59.2
65.0
59.9
62.9
63.4
61.1
50.9
41.7
48.6
125
65.3
61.1
61.2
61.6
71.4
54.8
62.6
49.4
43.0
50.0
160
62.5
61.4
63.0
34.4
75.1
63.9
58.3
46.3
44.2
50.4
200
54.9
56.8
62.7
56.4
68.5
60.2
61.5
46.5
42.9
48.4
250
55.6
59.5
59.6
57.3
67.6
62.3
70.1
45.7
39.3
47.9
315
54.9
55.9
56.0
46.9
66.8
60.3
72.8
38.5
36.7
52.3
400
51.7
55.7
59.0
42.9
66.4
57.7
66.2
33.9
34.0
37.7
500
50.1
48.2
59.4
40.4
67.0
49.8
49.9
34.3
27.8
42.2
630
44.0
39.6
52.1
28.4
58.2
39.6
45.3
30.3
19.3
43.5
800
30.2
32.9
46.8
19.9
45.3
32.9
33.5
28.3
11.8
29.4
1000
94.0
93.7
94.0
93.7
94.0
93.7
94.0
94.0
94.0
95.1
1250
28.9
28.9
31.0
28.4
32.3
28.8
29.4
29.2
29.1
30.0
1600
12.7
11.0
19.9
10.0
22.4
9.6
11.2
7.9
7.8
9.0
2000
35.4
34.6
35.2
35.5
35.3
35.6
35.6
35.3
34.8
36.0
2500
10.4
9.1
11.0
9.7
12.5
10.6
9.9
9.9
11.1
10.7
3150
43.5
43.2
43.7
43.1
43.6
43.2
43.4
43.2
43.4
44.5
4000
12.1
12.7
13.1
11.2
12.1
11.4
11.6
11.5
11.3
12.3
5000
15.6
14.7
16.5
14.3
15.3
16.6
14.9
15.0
15.5
16.0
6300
13.4
13.4
13.5
12.9
13.4
12.9
13.6
13.2
12.6
14.0
8000 10000 12500 16000 20000
14.4 15.2 16.6 17.4
14.7 15.3 16.7 17.5
14.6 16.1 16.6 17.7
14.3 15.3 16.2 17.6
15.1 16.1 16.7 17.7
14.4 15.8 16.4 17.2
14.5 15.1 16.1 17.8
14.7 15.6 16.7 17.3
14.5 15.1 16.4 17.6
15.5 16.3 17.7 18.4
12.5
62.0
67.7
57.7
16.0
59.3
61.8
56.9
20.0
62.7
66.4
58.4
25.0
58.4
63.3
53.8
31.5
60.2
63.6
55.1
40.0
61.8
64.6
59.2
50.0
72.5
75.1
62.8
63.0
69.7
71.9
66.1
80.0
65.3
67.1
60.0
100
71.0
75.0
66.4
125
75.6
76.7
71.2
160
67.3
68.8
65.7
200
67.4
68.4
66.3
250
70.9
72.8
69.7
315
67.2
70.4
66.3
400
68.8
70.0
67.6
500
63.7
64.7
58.0
630
64.8
68.2
63.7
800 1000 1250 1600
63.2 64.7 61.1 63.6
64.3 66.8 63.4 66.2
62.2 63.9 60.0 62.6
2000
56.6
57.1
56.0
2500
52.3
52.9
51.7
3150
51.8
55.6
50.5
4000
48.8
49.5
48.1
5000
48.7
52.3
47.8
6300
45.7
50.3
45.3
8000100001250016000 20000
44.9 42.7 40.5 38.6 32.3
46.8 44.6 41.9 39.2 33.1
44.5 42.1 40.0 38.1 31.7
Summary
Filename
Serial Number
Model
Firmware Version
User
Location
Job Description
Note
Start
Stop
Duration
Run Time
Pause
Pre Calibration
Post Calibration
Overall Settings
RMS Weight
Peak Weight
Detector
Preamp
Integration Method
OBA Range
OBA Bandwidth
OBA Freq. Weighting
OBA Max Spectrum
Overload
Under Range Peak
Under Range Limit
Noise Floor
Results
LASeq
LASE
EAS
EAS8
EAS40
LZpeak (max)
LASmax
LASmin
SEA
LCSeq
LASeq
LCSeq - LASeq
LAIeq
LAeq
LAIeq - LAeq
# Overloads
Overload Duration
# OBA Overloads
Dose Settings
Dose Name
Exch. Rate
Threshold
Criterion Level
Criterion Duration
LxT_Data.081
2471
LxT1
1.522
RH
CU 20 and CU21
Roof top
2013/10/10 12:43:15
2013/10/10 12:44:01
0:00:46.1
0:00:46.1
0:00:00.0
2013/10/10 11:21:20
None
---
A Weighting
Z Weighting
Slow
PRMLxT1L
Exponential
Normal
1/3 Octave
Z Weighting
Bin Max
121.9 dB
A
77.0
26.0
16.2
74.4
91.0
141.048
88.117
440.584
2013/10/10 12:43:15
2013/10/10 12:43:15
2013/10/10 12:43:55
-99.9
dB
dB
µPa²h
mPa²h
mPa²h
96.0 dB
75.3 dB
74.0 dB
dB
0
0
0
0
0
82.6
74.4
8.2
74.8
74.4
0.4
0
0.0
0
0.0
C
Z
74.0 79.0 dB
25.2 32.0 dB
16.0 21.9 dB
0.0
0.0
0.0
0.0
0.0
s
s
s
s
s
dB
dB
dB
dB
dB
dB
s
s
OSHA 1
5
None
90
8
OSHA 2
5
80
90
8
dB
dB
dB
h
Results
Dose
Projected Dose
TWA (Projected)
TWA (t)
Lep (t)
0.0
11.5
74.4
28.0
46.4
-99.9
-99.9
-99.9
-99.9
46.4
%
%
dB
dB
dB
Statistics
LAS5.00
LAS10.00
LAS33.30
LAS50.00
LAS66.30
LAS90.00
74.8
74.7
74.4
74.4
74.3
74.2
dB
dB
dB
dB
dB
dB
Calibration History
Preamp
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
1/3 Octave
Frequency (Hz)
Overall 1/3 Spectra
Max 1/3 Spectra
Min 1/3 Spectra
2013/10/10
2013/08/15
2013/08/15
2013/07/25
2013/07/25
2013/07/11
2013/07/11
2013/06/28
2013/06/27
2013/06/27
2013/05/03
Date
dB re. 1V/Pa
11:21:20
-27.9
12:57:41
-28.1
12:41:43
-27.9
15:00:18
-28.2
12:47:17
-27.9
14:00:51
-28.2
13:04:13
-27.9
11:57:52
-28.1
10:57:35
-28.1
10:57:11
-28.1
12:42:33
-29.2
6.3
61.0
67.5
54.4
8.0
63.0
69.0
56.4
10.0
62.9
66.2
57.3
6.3
65.1
70.3
69.4
79.0
67.4
78.1
65.8
46.5
43.9
41.9
8.0
62.4
67.7
71.2
71.8
56.4
66.1
79.0
55.9
51.1
47.0
10.0
54.3
72.8
58.0
53.9
58.2
62.2
70.5
63.3
54.6
55.5
12.5
64.9
72.5
69.3
53.0
65.4
69.9
68.2
61.4
61.4
61.3
16.0
51.5
72.0
63.2
64.6
60.1
70.1
63.6
59.2
61.1
57.5
20.0
55.0
68.5
66.4
69.6
65.6
72.9
63.9
50.6
54.9
58.0
25.0
61.1
68.7
71.8
61.8
64.7
62.2
59.5
54.4
53.0
46.5
31.5
68.4
74.5
69.9
61.2
62.9
69.6
62.5
50.9
48.5
60.1
40.0
76.5
64.5
80.9
57.2
64.1
56.8
53.8
54.0
46.1
56.3
50.0
72.5
62.2
66.4
50.7
63.5
54.3
55.8
49.1
59.2
52.8
63.0
68.4
66.7
70.2
50.6
65.9
63.4
57.7
48.4
49.4
62.7
80.0
71.4
58.4
74.3
43.5
67.9
61.3
62.4
45.8
46.9
62.2
100
58.9
59.2
65.0
59.9
62.9
63.4
61.1
50.9
41.7
48.6
125
65.3
61.1
61.2
61.6
71.4
54.8
62.6
49.4
43.0
50.0
160
62.5
61.4
63.0
34.4
75.1
63.9
58.3
46.3
44.2
50.4
200
54.9
56.8
62.7
56.4
68.5
60.2
61.5
46.5
42.9
48.4
250
55.6
59.5
59.6
57.3
67.6
62.3
70.1
45.7
39.3
47.9
315
54.9
55.9
56.0
46.9
66.8
60.3
72.8
38.5
36.7
52.3
400
51.7
55.7
59.0
42.9
66.4
57.7
66.2
33.9
34.0
37.7
500
50.1
48.2
59.4
40.4
67.0
49.8
49.9
34.3
27.8
42.2
630
44.0
39.6
52.1
28.4
58.2
39.6
45.3
30.3
19.3
43.5
800
30.2
32.9
46.8
19.9
45.3
32.9
33.5
28.3
11.8
29.4
1000
94.0
93.7
94.0
93.7
94.0
93.7
94.0
94.0
94.0
95.1
1250
28.9
28.9
31.0
28.4
32.3
28.8
29.4
29.2
29.1
30.0
1600
12.7
11.0
19.9
10.0
22.4
9.6
11.2
7.9
7.8
9.0
2000
35.4
34.6
35.2
35.5
35.3
35.6
35.6
35.3
34.8
36.0
2500
10.4
9.1
11.0
9.7
12.5
10.6
9.9
9.9
11.1
10.7
3150
43.5
43.2
43.7
43.1
43.6
43.2
43.4
43.2
43.4
44.5
4000
12.1
12.7
13.1
11.2
12.1
11.4
11.6
11.5
11.3
12.3
5000
15.6
14.7
16.5
14.3
15.3
16.6
14.9
15.0
15.5
16.0
6300
13.4
13.4
13.5
12.9
13.4
12.9
13.6
13.2
12.6
14.0
8000 10000 12500 16000 20000
14.4 15.2 16.6 17.4
14.7 15.3 16.7 17.5
14.6 16.1 16.6 17.7
14.3 15.3 16.2 17.6
15.1 16.1 16.7 17.7
14.4 15.8 16.4 17.2
14.5 15.1 16.1 17.8
14.7 15.6 16.7 17.3
14.5 15.1 16.4 17.6
15.5 16.3 17.7 18.4
12.5
62.0
67.4
56.1
16.0
63.2
65.8
59.9
20.0
65.2
68.5
58.2
25.0
61.8
65.2
58.5
31.5
65.9
68.8
59.8
40.0
63.4
66.2
60.2
50.0
70.4
73.4
66.8
63.0
70.7
73.3
66.4
80.0
70.4
73.5
66.2
100
67.2
69.6
65.5
125
77.4
78.7
73.0
160
70.8
72.8
69.4
200
70.3
71.8
69.2
250
75.2
76.3
74.2
315
67.8
69.1
65.9
400
68.4
70.1
65.0
500
64.8
66.7
63.6
630
62.9
64.5
61.6
800 1000 1250 1600
64.1 66.5 59.8 65.4
65.7 67.5 60.7 66.1
62.5 63.6 57.9 64.5
2000
58.8
60.4
57.4
2500
53.8
54.5
52.0
3150
53.7
54.2
53.0
4000
52.1
52.6
51.0
5000
50.3
51.0
49.8
6300
49.5
50.2
49.0
8000100001250016000 20000
50.2 47.7 44.6 40.2 34.9
51.1 48.3 45.6 40.9 35.8
49.7 46.8 43.1 39.5 33.9
Summary
Filename
Serial Number
Model
Firmware Version
User
Location
Job Description
Note
Start
Stop
Duration
Run Time
Pause
Pre Calibration
Post Calibration
Overall Settings
RMS Weight
Peak Weight
Detector
Preamp
Integration Method
OBA Range
OBA Bandwidth
OBA Freq. Weighting
OBA Max Spectrum
Overload
Under Range Peak
Under Range Limit
Noise Floor
Results
LASeq
LASE
EAS
EAS8
EAS40
LZpeak (max)
LASmax
LASmin
SEA
LCSeq
LASeq
LCSeq - LASeq
LAIeq
LAeq
LAIeq - LAeq
# Overloads
Overload Duration
# OBA Overloads
Dose Settings
Dose Name
Exch. Rate
Threshold
Criterion Level
Criterion Duration
LxT_Data.082
2471
LxT1
1.522
RH
CU-23
Roof top
2013/10/10 12:45:44
2013/10/10 12:46:31
0:00:47.2
0:00:47.2
0:00:00.0
2013/10/10 11:21:20
None
---
A Weighting
Z Weighting
Slow
PRMLxT1L
Exponential
Normal
1/3 Octave
Z Weighting
Bin Max
121.9 dB
A
C
77.0 74.0
26.0 25.2
16.2 16.0
75.5
92.3
187.374
114.330
571.650
2013/10/10 12:45:44
2013/10/10 12:45:49
2013/10/10 12:45:44
-99.9
dB
dB
µPa²h
mPa²h
mPa²h
97.5 dB
75.9 dB
74.1 dB
dB
0
0
0
0
0
82.2
75.5
6.7
76.1
75.6
0.5
0
0.0
0
0.0
0.0
0.0
0.0
0.0
0.0
0.0
13.4
75.5
29.3
47.7
Statistics
LAS5.00
LAS10.00
LAS33.30
LAS50.00
LAS66.30
LAS90.00
75.8
75.8
75.7
75.6
75.5
75.2
s
s
s
s
s
dB
dB
dB
dB
dB
dB
s
s
OSHA 1OSHA 2
5
5
None
80
90
90
8
8
Results
Dose
Projected Dose
TWA (Projected)
TWA (t)
Lep (t)
Z
79.0 dB
32.0 dB
21.9 dB
-99.9
-99.9
-99.9
-99.9
47.7
dB
dB
dB
dB
dB
dB
dB
dB
dB
h
%
%
dB
dB
dB
Calibration History
Preamp
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
PRMLxT1L
1/3 Octave
Frequency (Hz)
Overall 1/3 Spectra
Max 1/3 Spectra
Min 1/3 Spectra
2013/10/10
2013/08/15
2013/08/15
2013/07/25
2013/07/25
2013/07/11
2013/07/11
2013/06/28
2013/06/27
2013/06/27
2013/05/03
dB
Date
re. 1V/Pa
11:21:20 -27.9
12:57:41 -28.1
12:41:43 -27.9
15:00:18 -28.2
12:47:17 -27.9
14:00:51 -28.2
13:04:13 -27.9
11:57:52 -28.1
10:57:35 -28.1
10:57:11 -28.1
12:42:33 -29.2
6.3
66.6
74.5
56.4
8.0
67.8
73.4
60.4
10.0
69.3
75.5
58.5
6.3
65.1
70.3
69.4
79.0
67.4
78.1
65.8
46.5
43.9
41.9
8.0
62.4
67.7
71.2
71.8
56.4
66.1
79.0
55.9
51.1
47.0
10.0
54.3
72.8
58.0
53.9
58.2
62.2
70.5
63.3
54.6
55.5
12.5
64.9
72.5
69.3
53.0
65.4
69.9
68.2
61.4
61.4
61.3
16.0
51.5
72.0
63.2
64.6
60.1
70.1
63.6
59.2
61.1
57.5
20.0
55.0
68.5
66.4
69.6
65.6
72.9
63.9
50.6
54.9
58.0
25.0
61.1
68.7
71.8
61.8
64.7
62.2
59.5
54.4
53.0
46.5
31.5
68.4
74.5
69.9
61.2
62.9
69.6
62.5
50.9
48.5
60.1
40.0
76.5
64.5
80.9
57.2
64.1
56.8
53.8
54.0
46.1
56.3
50.0
72.5
62.2
66.4
50.7
63.5
54.3
55.8
49.1
59.2
52.8
63.0
68.4
66.7
70.2
50.6
65.9
63.4
57.7
48.4
49.4
62.7
80.0
71.4
58.4
74.3
43.5
67.9
61.3
62.4
45.8
46.9
62.2
100
58.9
59.2
65.0
59.9
62.9
63.4
61.1
50.9
41.7
48.6
125
65.3
61.1
61.2
61.6
71.4
54.8
62.6
49.4
43.0
50.0
160
62.5
61.4
63.0
34.4
75.1
63.9
58.3
46.3
44.2
50.4
200
54.9
56.8
62.7
56.4
68.5
60.2
61.5
46.5
42.9
48.4
250
55.6
59.5
59.6
57.3
67.6
62.3
70.1
45.7
39.3
47.9
315
54.9
55.9
56.0
46.9
66.8
60.3
72.8
38.5
36.7
52.3
400
51.7
55.7
59.0
42.9
66.4
57.7
66.2
33.9
34.0
37.7
500
50.1
48.2
59.4
40.4
67.0
49.8
49.9
34.3
27.8
42.2
630
44.0
39.6
52.1
28.4
58.2
39.6
45.3
30.3
19.3
43.5
800
30.2
32.9
46.8
19.9
45.3
32.9
33.5
28.3
11.8
29.4
1000
94.0
93.7
94.0
93.7
94.0
93.7
94.0
94.0
94.0
95.1
1250
28.9
28.9
31.0
28.4
32.3
28.8
29.4
29.2
29.1
30.0
1600
12.7
11.0
19.9
10.0
22.4
9.6
11.2
7.9
7.8
9.0
2000
35.4
34.6
35.2
35.5
35.3
35.6
35.6
35.3
34.8
36.0
2500
10.4
9.1
11.0
9.7
12.5
10.6
9.9
9.9
11.1
10.7
3150
43.5
43.2
43.7
43.1
43.6
43.2
43.4
43.2
43.4
44.5
4000
12.1
12.7
13.1
11.2
12.1
11.4
11.6
11.5
11.3
12.3
5000
15.6
14.7
16.5
14.3
15.3
16.6
14.9
15.0
15.5
16.0
6300
13.4
13.4
13.5
12.9
13.4
12.9
13.6
13.2
12.6
14.0
8000 10000 12500 16000 20000
14.4 15.2 16.6 17.4
14.7 15.3 16.7 17.5
14.6 16.1 16.6 17.7
14.3 15.3 16.2 17.6
15.1 16.1 16.7 17.7
14.4 15.8 16.4 17.2
14.5 15.1 16.1 17.8
14.7 15.6 16.7 17.3
14.5 15.1 16.4 17.6
15.5 16.3 17.7 18.4
12.5
71.2
75.3
65.7
16.0
68.4
72.7
64.2
20.0
69.8
72.1
67.1
25.0
66.2
69.5
60.4
31.5
66.7
70.1
62.7
40.0
67.7
70.6
64.9
50.0
72.5
76.1
67.8
63.0
71.5
73.4
69.8
80.0
67.8
70.1
64.9
100
68.3
70.6
66.2
125
72.2
75.9
68.2
160
66.0
67.6
64.3
200
64.6
66.3
56.2
250
65.0
66.4
62.7
315
74.7
75.4
73.8
400
76.6
77.5
74.4
500
63.8
65.2
60.1
630
63.0
64.0
58.5
800
65.4
66.8
63.7
1000
64.3
67.3
63.1
1250
59.4
62.3
58.4
1600
59.1
60.3
58.1
2000
58.4
59.2
55.1
2500
57.4
58.7
56.3
3150
56.6
57.5
55.8
4000
55.3
57.3
52.5
5000
52.7
53.3
49.1
6300
55.5
57.2
54.8
8000100001250016000 20000
53.0 49.8 49.3 46.3 42.3
54.2 51.6 50.9 47.2 43.3
52.4 49.1 48.6 45.7 41.5
SPL to PWL calculation of measurements
Reefer Truck
2
Noise Source
Distance
Parameters
read 1
octave band
Sludge tanks -ST1
2
PWL
read 1
86
97
94
85
80
80
78
73
65
octave band
Barn fans-BF1
3
PWL
read 1
75
83
73
72
74
74
70
65
58
octave band
Blower Louver
3
PWL
read 1
95
88
86
80
81
80
80
73
64
address ID
67
68
70
69
31.5 Hz
72
83
80
71
66
66
64
59
51
61
69
59
58
60
60
56
51
44
78
71
69
62
63
63
62
55
47
62
65
65
68
77
71
71
56
49
63 Hz
125 Hz
250 Hz
500 Hz
1 kHz
2 kHz
4 kHz
8 kHz
72
83
80
71
66
66
64
59
51
61
69
59
58
60
60
56
51
44
78
71
69
62
63
63
62
55
47
octave band
PWL
62
65
65
68
77
71
71
56
49
80
83
82
86
94
88
89
74
66
3
Noise Source
Distance
Parameters
read 1
address ID
74
31.5 Hz
66
75
74
67
70
722
72
67
56
63 Hz
125 Hz
250 Hz
500 Hz
1 kHz
2 kHz
4 kHz
8 kHz
octave band
make up air unit-RTU21&RTU22
3
PWL
read 1
octave band
PWL
71
66
75
74
67
70
72
72
67
56
83
92
92
85
88
90
89
84
73
71
71
60
56
55
57
53
49
41
Truck backing into barn area
4
read 1
octave band
PWL
72
71
71
60
56
55
57
53
49
41
88
89
77
74
72
75
71
66
59
71
74
66
59
63
64
62
60
59
truck parked (Hogs noise) - being unloaded
3
read 1
octave band
PWL
73
71
74
66
59
63
64
62
60
59
91
94
86
79
83
84
82
80
79
65
71
70
61
62
66
57
52
48
Air intake
2
read 1
octave band
quickwater boiler exhaust ES4 & ES5
3
PWL
75
65
71
70
61
62
66
57
52
48
83
89
87
79
79
84
74
69
65
79
79
72
64
65
62
61
52
50
read 1
octave band
PWL
80
75
74
65
59
56
51
44
38
97
93
92
82
76
74
69
62
55
76
79
79
72
64
65
62
61
52
50
93
93
86
78
79
76
75
66
64
80
75
74
65
59
56
6
51
44
38
condensing units CU5,6,7
6
Noise Source
Distance
Parameters
read 1
address ID
77
31.5 Hz
66
72
71
68
64
63
58
55
50
63 Hz
125 Hz
250 Hz
500 Hz
1 kHz
kH
2 kHz
4 kHz
8 kHz
condensing units CU11
3
octave band
PWL
read 1
66
72
71
68
64
63
58
55
50
90
95
95
91
87
86
81
79
74
64
70
74
75
66
64
57
52
50
CU-12 and CU-13
2
octave band
PWL
read 1
64
70
74
75
66
64
57
52
50
80
86
90
91
82
80
73
68
66
60
68
67
67
60
61
56
54
44
78
CU-18 and CU-19
2
octave band
PWL
read 1
60
68
67
67
60
61
56
54
44
74
82
81
81
74
75
70
68
58
60
70
76
71
64
65
57
49
45
79
CU-20 and CU-21
2
octave band
PWL
read 1
60
70
76
71
64
65
57
49
45
74
84
90
85
78
79
71
63
59
66
71
77
75
65
67
59
52
50
89
CU-23
2
octave band
PWL
read 1
66
71
77
75
65
67
59
52
50
80
85
91
89
79
81
73
66
64
67
72
72
65
64
64
58
55
53
81
octave band
PWL
67
72
72
65
64
64
58
55
53
81
86
86
79
78
78
72
69
67
82
Weather condition during measurements on October 10, 2013
Station Name
Province
Latitude
Longitude
Elevation
Climate Identifier
WMO Identifier
TC Identifier
M
Date/Time
10/10/2013 0:00
10/10/2013 1:00
10/10/2013 2:00
10/10/2013 3:00
10/10/2013 4:00
10/10/2013 5:00
10/10/2013 6:00
10/10/2013 7:00
10/10/2013 8:00
10/10/2013 9:00
10/10/2013 10:00
10/10/2013 11:00
10/10/2013 12:00
10/10/2013 13:00
10/10/2013 14:00
10/10/2013 15:00
10/10/2013 16:00
10/10/2013 17:00
10/10/2013 18:00
10/10/2013 19:00
10/10/2013 20:00
10/10/2013 21:00
10/10/2013 22:00
10/10/2013 23:00
KITCHENER/WATERLOO
ONTARIO
43.46
-80.38
321.6
6144239
71368
YKF
Missing
Year
Month
Day
Time
Data
Quality
Temp (°C)
2013
2013
2013
2013
2013
2013
2013
2013
2013
2013
2013
2013
2013
2013
2013
2013
2013
2013
2013
2013
2013
2013
2013
2013
10
10
10
10
10
10
10
10
10
10
10
10
10
10
10
10
10
10
10
10
10
10
10
10
10
10
10
10
10
10
10
10
10
10
10
10
10
10
10
10
10
10
10
10
10
10
10
10
0:00
1:00
2:00
3:00
4:00
5:00
6:00
7:00
8:00
9:00
10:00
11:00
12:00
13:00
14:00
15:00
16:00
17:00
18:00
19:00
20:00
21:00
22:00
23:00
**
**
**
**
**
**
**
**
**
**
**
**
**
**
**
**
**
**
**
**
**
**
**
**
5
5
4
4
6
7
7
6
7
9
12
16
19
20
20
21
20
17
14
10
8
8
7
6
Dew Point Rel Hum
Temp (°C)
(%)
5
5
4
4
5
7
7
6
7
8
11
10
10
6
7
7
9
8
8
7
6
6
5
5
99
99
99
99
98
98
98
98
98
98
95
68
55
39
43
41
48
56
66
85
86
87
89
96
Wind Dir
(10s deg)
Wind Dir
Flag
31
34
35
M
6
11
8
12
13
11
9
7
7
9
5
Wind Spd
(km/h)
Visibility
(km)
Stn Press
(kPa)
Weather
0
4
0
5
0
0
8
0
0
0
0
4
13
17
9
9
15
15
5
5
5
8
4
0
0
1
0
1
1
0
0
0
0
0
16
16
16
16
16
16
16
16
16
16
16
16
16
10
99
99
99
99
99
99
99
99
99
99
99
99
99
98
98
98
98
98
98
98
98
98
98
98
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
NA
Sound Data
800DFHB
60Hz
Sound Pressure Levels @ 7 meters dB(A)
Configuration
Standard-Unhoused (Note 3)
F200 - Weather
F201 - Quiet Site II First Stage
F202 - Quiet Site II Second
Stage
Note:
1.
2.
3.
4.
5.
6.
7.
Infinite
Exhaust
Mounted
Muffler
Mounted
Muffler
Mounted
Muffler
Position (Note 1)
4
5
6
7
8
8 Position
Average
93
N/A
95
N/A
95
90.4
94.7
92.6
82.6
94.5
91.2
77.7
80.1
87.6
83.3
76.9
81.2
81.3
77.7
80.1
87.6
83.3
76.9
81.2
81.3
1
2
3
96
N/A
95
N/A
94
93.4
84
82.2
79.8
82.2
79.8
Position 1 faces the engine front at 23 feet (7 m) from the surface of the generator set. The positions proceed around the generator set in a
counter-clockwise direction in 45° increments.
Data based on full rated load with standard radiator-fan package.
Sound data for generator set with infinite exhaust do not include exhaust noise.
Sound pressure levels per ANSI S1.13-1971 as applicable.
Reference sound pressure is 10 µPa.
Sound pressure levels are subject to instrumentation, measurement, installation and generator set variability.
Sound data with remote-cooled sets are based on rated loads without fan noise.
Sound Power Levels dB(A)
Octave Band Center Frequency (Hz)
Configuration
Standard-Unhoused (Note 3)
F200 - Weather
F201 - Quiet Site II First Stage
F202 - Quiet Site II Second Stage
Note:
1.
2.
3.
4.
5.
6.
Infinite
Exhaust
Mounted
Muffler
Mounted
Muffler
Mounted
Muffler
Sound Power
Level
63
125
250
500
1000
2000
4000
8000
78.8
101
107.1
109
112.7
111.5
107.4
100
122.2
80.7
93.8
104.8
106.9
109.6
107.9
102
93.3
118.8
80.4
96.1
100.5
99.8
101.9
100.2
96.4
86.5
112.1
80.8
95.6
95.8
90.7
96.2
98.8
97.3
85.4
108.9
Sound pressure levels per ANSI S12.34-1988 and SIO 3744 as applicable.
Data based on full rated load with standard radiator-fan package.
Sound data for generator set with infinite exhaust do not include exhaust noise.
-12
Reference sound pressure is 1pW-1x10 W.
Sound pressure levels are subject to instrumentation, measurement, installation and generator set variability.
Sound data with remote-cooled sets are based on rated loads without fan noise.
Exhaust Sound Pressure Levels @ 1 meter dB(A)
Octave Band Center Frequency (Hz)
Open Exhaust (No Muffler) @ Rated Load
63
N/A
125
N/A
250
N/A
500
N/A
1000
N/A
2000
N/A
4000
N/A
8000
N/A
Sound
Pressure Level
N/A
Note: Sound pressure level per ISO 6798 Annex A as applicable.
Cummins Power Generation
Data and Specification Subject to Change Without Notice
Bulletin msp-150e
Sound Pressure Levels (SPL) in dB RE 0.0002 Microbar
Sound Power Levels (PWL) in dB RE 10-12 Watt
MODEL
ATC-XC669E-1g
MOTOR
40.00 HP
# MOTORS
SPEED:
1
Full Speed
1 CELL DATA
SOUND PRESSURE LEVEL (dB)
End
5 ft
BAND
Motor Side
50 ft
5 ft
50 ft
Opp End
5 ft
Opp Mtr. Side
50 ft
5 ft
50 ft
Top
5 ft
SOUND
50 ft
(1.5m) (15m) (1.5m) (15m) (1.5m) (15m) (1.5m) (15m) (1.5m) (15m)
POWER
LEVEL (dB)
63 HZ
72
68
72
68
72
68
72
68
80
71
101
125 HZ
80
69
80
69
80
69
80
69
82
72
102
250 HZ
80
68
80
68
80
68
80
68
83
73
102
500 HZ
75
61
76
61
75
61
76
61
79
68
96
1 KHZ
73
58
72
59
73
58
72
59
74
61
91
2 KHZ
70
54
70
56
70
54
70
56
73
59
88
4 KHZ
71
53
71
53
71
53
71
53
75
58
87
8 KHZ
72
52
72
53
72
52
72
53
71
54
85
CALC
dBA
80
65
80
65
80
65
80
65
82
70
99
Sound option(s) selected: None
January 2014
APPENDIX E
INSIGNIFICANT NOISE SOURCES
TR1213003
Summary of Insignificant Noise Sources
Project:
Location:
CMP
Breslau, Ontario
Source ID
Source Description
Reason/Rational
EF1 to EF53
CU1 to CU4
ES1 to ES3 & ES6 to EF14
RTU1 to RTU20 & RTU23
Exhaust Stack
Condensing Unit
Boiler Stack
Roof top Unit
Quiet Units
Quiet Units
Quiet Units
Quiet Units
January 2014
APPENDIX F
KEY PARAMETERS USED IN THE ASSESSMENT AND SAMPLE CALCULATIONS
TR1213003
Key Parameters Included in the Noise Model
Project:
Location:
Parameter
Ground Absorption
Temperature
Relative Humidity
Max. Order of Reflection
CMP
Breslau, Ontario
Value
0.7
10°C
70%
1
Rationale
Accounts for mostly soft (e.g., grass) surfaces and limited hard (e.g., packed dirt, pavement
and gravel) surfacesbetween facility and receptors of interest.
Ontario standard conditions
Ontario standard conditions
Accounts building reflections
Receiver
Name:
Two-storey residential dwelling located approximately 200 m south of the facility
ID: POR1
X:
549182.66
Y:
4813218.48
Z:
4.50
Nr.
1
Nr.
1
Nr.
1
Nr.
1
Nr.
1
Nr.
1
Nr.
1
Nr.
1
X
Y
(m)
(m)
549190.22 4813535.76
Point Source, ISO 9613, Name: ''Air Intake'', ID: ''AIR1''
Z
Refl. Freq. LxT LxN K0 Dc Adiv Aatm Agr Afol Ahous Abar Cmet RL LrT LrN
(m)
(Hz) dB(A) dB(A) (dB) (dB) (dB) (dB) (dB) (dB) (dB) (dB) (dB) (dB) dB(A) dB(A)
15.36
0
0 81.8 81.8 0.0 0.0 61.0 1.5 -0.8 0.0
0.0 0.0 -0.0 -0.0 20.1 20.1
X
Y
(m)
(m)
549154.56 4813493.49
Point Source, ISO 9613, Name: ''Barn Fan '', ID: ''BF''
Z
(m)
4.00
0
0 85.4 85.4 0.0 0.0 59.8 1.7 -0.8 0.0
0.0 0.0 -0.0 -0.0 24.6 24.6
X
Y
(m)
(m)
549245.25 4813529.14
Point Source, ISO 9613, Name: ''Condensing unit 11'', ID: ''CU11''
Z
(m)
9.00
0
0 86.2 86.2 0.0 0.0 61.0 0.8 -0.3 0.0
0.0 4.6 -0.0 -0.0 20.0 20.0
X
Y
(m)
(m)
549265.93 4813560.22
Point Source, ISO 9613, Name: ''Condensing Unit 12&13'', ID: ''CU12''
Z
(m)
12.00
0
0 79.4 79.4 0.0 0.0 61.9 1.6 -0.6 0.0
0.0 0.0 -0.0 -0.0 16.4 16.4
X
Y
(m)
(m)
549275.49 4813518.12
Point Source, ISO 9613, Name: ''Condensing Unit 18'', ID: ''CU18''
Z
(m)
9.00
0
0 83.0 83.0 0.0 0.0 60.9 0.9 -0.3 0.0
0.0 4.5 -0.0 -0.0 16.9 16.9
X
Y
(m)
(m)
549272.44 4813501.84
Z
(m)
9.00
0
0 85.3 85.3 0.0 0.0 60.5 0.9 -0.4 0.0
0.0 0.0 -0.0 -0.0 24.3 24.3
X
Y
(m)
(m)
549246.30 4813494.60
Z
(m)
10.00
0
0 81.8 81.8 0.0 0.0 60.0 1.4 -0.7 0.0
0.0 0.0 -0.0 -0.0 21.0 21.0
X
Y
(m)
(m)
549211.32 4813440.01
Point Source, ISO 9613, Name: ''Condnsing Unit 24-Top'', ID: ''CU24''
Z
(m)
12.10
0
0 93.8 93.8 0.0 0.0 58.0 2.0 -0.6 0.0
0.0 0.0 -0.0 -0.0 34.5 34.5
Page1
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1
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1
Nr.
1
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1
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1
Nr.
1
Nr.
1
Nr.
1
Point Source, ISO 9613, Name: ''Condensing Unit 24-Side 1'', ID: ''CU24-S1''
X
Y
Z
(m)
(m)
(m)
549208.94 4813438.82
9.50
0
0 91.2 91.2 3.0 0.0 57.9 2.1 -0.6 0.0
0.0 0.0 -0.0 -0.0 34.8 34.8
X
Y
Z
(m)
(m)
(m)
549212.04 4813438.63
9.50
0
0 91.2 91.2 3.0 0.0 57.9 2.1 -0.6 0.0
0.0 0.0 -0.0 -0.0 34.8 34.8
X
Y
Z
(m)
(m)
(m)
549213.95 4813441.26
9.50
0
0 91.2 91.2 3.0 0.0 58.0 2.1 -0.4 0.0
0.0 8.7 -0.0 -0.0 25.7 25.7
X
Y
Z
(m)
(m)
(m)
549210.74 4813441.37
9.50
0
0 91.2 91.2 3.0 0.0 58.0 2.1 -0.2 0.0
0.0 13.4 -0.0 -0.0 20.8 20.8
X
Y
(m)
(m)
549217.02 4813442.69
Point Source, ISO 9613, Name: ''Condensing Unit 25-Top'', ID: ''CU25''
Z
(m)
12.10
0
0 93.8 93.8 0.0 0.0 58.1 2.0 -0.6 0.0
0.0 0.0 -0.0 -0.0 34.4 34.4
X
Y
Z
(m)
(m)
(m)
549214.42 4813441.56
9.50
0
0 91.2 91.2 3.0 0.0 58.1 2.1 -0.5 0.0
0.0 5.5 -0.0 -0.0 29.0 29.0
X
Y
Z
(m)
(m)
(m)
549217.72 4813441.29
9.50
0
0 91.2 91.2 3.0 0.0 58.1 2.1 -0.6 0.0
0.0 0.0 -0.0 -0.0 34.6 34.6
X
Y
Z
(m)
(m)
(m)
549219.81 4813443.97
9.50
0
0 91.2 91.2 3.0 0.0 58.2 2.1 -0.1 0.0
0.0 15.2 -0.0 -0.0 18.8 18.8
X
Y
Z
(m)
(m)
(m)
549216.48 4813444.06
9.50
0
0 91.2 91.2 3.0 0.0 58.2 2.1 -0.1 0.0
0.0 16.1 -0.0 -0.0 17.9 17.9
X
Y
(m)
(m)
549220.25 4813435.74
Z
(m)
12.10
0
0 93.8 93.8 0.0 0.0 57.9 1.9 -0.6 0.0
0.0 0.0 -0.0 -0.0 34.6 34.6
Page2
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1
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1
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1
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1
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1
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1
Nr.
1
Nr.
1
X
Y
Z
(m)
(m)
(m)
549217.94 4813434.70
9.50
0
0 91.2 91.2 3.0 0.0 57.8 2.1 -0.6 0.0
0.0 0.0 -0.0 -0.0 34.9 34.9
X
Y
Z
(m)
(m)
(m)
549220.85 4813434.33
9.50
0
0 91.2 91.2 3.0 0.0 57.8 2.1 -0.6 0.0
0.0 0.0 -0.0 -0.0 34.9 34.9
X
Y
Z
(m)
(m)
(m)
549222.93 4813437.08
9.50
0
0 91.2 91.2 3.0 0.0 57.9 2.1 -0.3 0.0
0.0 9.4 -0.0 -0.0 25.1 25.1
X
Y
Z
(m)
(m)
(m)
549219.61 4813437.11
9.50
0
0 91.2 91.2 3.0 0.0 57.9 2.1 -0.2 0.0
0.0 13.1 -0.0 -0.0 21.3 21.3
X
Y
(m)
(m)
549230.95 4813502.12
Z
(m)
6.70
0
0 90.8 90.8 0.0 0.0 60.2 0.8 -0.2 0.0
0.0 8.1 -0.0 -0.0 21.9 21.9
X
Y
(m)
(m)
549232.42 4813497.57
Z
(m)
6.70
0
0 90.8 90.8 0.0 0.0 60.0 0.8 -0.1 0.0
0.0 11.9 -0.0 -0.0 18.1 18.1
X
Y
(m)
(m)
549234.69 4813492.22
Z
(m)
6.70
0
0 90.8 90.8 0.0 0.0 59.9 0.8 -0.2 0.0
0.0 9.5 -0.0 -0.0 20.7 20.7
X
Y
(m)
(m)
549220.28 4813518.22
Point Source, ISO 9613, Name: ''Condensing Unit 5&6&7'', ID: ''CU5''
Z
(m)
9.00
0
0 90.7 90.7 0.0 0.0 60.6 1.4 -0.4 0.0
0.0 5.1 -0.0 -0.0 24.0 24.0
X
Y
(m)
(m)
549188.96 4813537.86
Point Source, ISO 9613, Name: ''Quickwater boiler exhaust'', ID: ''ES4''
Z
(m)
17.30
0
0 80.9 80.9 0.0 0.0 61.1 0.7 -0.2 0.0
0.0 0.0 -0.0 -0.0 19.3 19.3
X
Y
(m)
(m)
549136.23 4813509.80
Point Source, ISO 9613, Name: ''Hogs Noise'', ID: ''HN''
Z
(m)
2.00
0
0 85.6 85.6 0.0 0.0 60.4 1.2 -0.8 0.0
0.0 0.0 -0.0 -0.0 24.7 24.7
Page3
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1
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1
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1
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1
Nr.
1
Nr.
1
Nr.
1
Nr.
1
X
Y
(m)
(m)
549151.79 4813497.12
Point Source, ISO 9613, Name: ''Truck unloading hogs'', ID: ''HT''
Z
(m)
2.00
0
0 94.4 94.4 0.0 0.0 59.9 2.0 -0.7 0.0
0.0 4.5 -0.0 -0.0 28.6 28.6
X
Y
(m)
(m)
549373.25 4813530.25
Point Source, ISO 9613, Name: ''Blower Louver'', ID: ''LV1''
Z
(m)
3.66
0
0 94.7 94.7 0.0 0.0 62.3 1.7 -1.1 0.0
0.0 0.0 -0.0 -0.0 31.9 31.9
X
Y
(m)
(m)
549208.69 4813432.66
Point Source, ISO 9613, Name: ''Compressor Louver 2'', ID: ''LV2''
Z
(m)
1.50
0
0 84.8 84.8 0.0 0.0 57.7 0.9 1.0 0.0
0.0 0.0 -0.0 -0.0 25.3 25.3
X
Y
(m)
(m)
549206.79 4813436.73
Z
(m)
3.66
0
0 84.8 84.8 0.0 0.0 57.8 0.9 -0.7 0.0
0.0 0.0 -0.0 -0.0 26.8 26.8
X
Y
(m)
(m)
549205.10 4813440.45
Z
(m)
5.00
0
0 84.8 84.8 0.0 0.0 58.0 0.9 -0.8 0.0
0.0 0.0 -0.0 -0.0 26.8 26.8
X
Y
(m)
(m)
549225.57 4813552.57
Point Source, ISO 9613, Name: ''Reefer Trailer 1'', ID: ''R1''
Z
(m)
4.00
0
0 85.8 85.8 0.0 0.0 61.5 1.4 0.9 0.0
0.0 13.4 -0.0 -0.0
8.5
8.5
X
Y
(m)
(m)
549229.19 4813554.78
Z
(m)
4.00
0
0 85.8 85.8 0.0 0.0 61.6 1.5 0.9 0.0
0.0 12.6 -0.0 -0.0
9.3
9.3
X
Y
(m)
(m)
549232.36 4813556.62
Z
(m)
4.00
0
0 85.8 85.8 0.0 0.0 61.7 1.5 0.9 0.0
0.0 11.6 -0.0 -0.0 10.2 10.2
X
Y
(m)
(m)
549235.96 4813558.54
Z
(m)
4.00
0
0 85.8 85.8 0.0 0.0 61.7 1.5 0.9 0.0
0.0 11.2 -0.0 -0.0 10.5 10.5
X
Y
(m)
(m)
549240.10 4813560.37
Z
(m)
4.00
0
0 85.8 85.8 0.0 0.0 61.8 1.5 0.9 0.0
0.0 11.2 -0.0 -0.0 10.4 10.4
Page4
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1
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1
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1
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1
Nr.
1
Nr.
1
Nr.
1
Nr.
1
2
Nr.
1
2
X
Y
(m)
(m)
549243.45 4813562.33
Z
(m)
4.00
0
0 85.8 85.8 0.0 0.0 61.9 1.5 0.9 0.0
0.0 11.1 -0.0 -0.0 10.4 10.4
X
Y
(m)
(m)
549246.30 4813563.67
Z
(m)
4.00
0
0 85.8 85.8 0.0 0.0 61.9 1.5 0.9 0.0
0.0 11.0 -0.0 -0.0 10.4 10.4
X
Y
(m)
(m)
549323.89 4813585.08
Z
(m)
4.00
0
0 85.8 85.8 0.0 0.0 62.9 1.6 0.1 0.0
0.0 2.1 -0.0 -0.0 19.0 19.0
X
Y
(m)
(m)
549295.33 4813516.61
Z
(m)
4.00
0
0 85.8 85.8 0.0 0.0 61.1 1.4 0.5 0.0
0.0 10.4 -0.0 -0.0 12.4 12.4
X
Y
(m)
(m)
549141.82 4813532.08
Point Source, ISO 9613, Name: ''make up air unit 21'', ID: ''RTU21''
Z
(m)
4.00
0
0 78.3 78.3 0.0 0.0 61.0 1.7 -1.2 0.0
0.0 12.2 -0.0 -0.0
4.6
4.6
X
Y
(m)
(m)
549150.85 4813539.43
Point Source, ISO 9613, Name: ''Air make up unit 22'', ID: ''RTU22''
Z
(m)
4.00
0
0 78.3 78.3 0.0 0.0 61.2 1.7 -1.5 0.0
0.0 16.8 -0.0 -0.0
0.2
0.2
X
Y
(m)
(m)
549364.70 4813559.58
Point Source, ISO 9613, Name: ''Sludge Tanks'', ID: ''ST''
Z
(m)
0.00
0
0 77.6 77.6 0.0 0.0 62.8 2.0 2.0 0.0
0.0 0.0 -0.0 -0.0 10.9 10.9
X
Y
(m)
(m)
549120.30 4813493.26
549146.44 4813495.39
Line Source, ISO 9613, Name: ''Truck Route 1'', ID: ''TR1''
Z
(m)
2.00
0
0 81.5 81.5 0.0 0.0 60.0 1.4 -0.6 0.0
0.0 0.0 -0.0 -0.0 20.7 20.7
2.00
0
0 72.0 72.0 0.0 0.0 59.9 1.4 -0.5 0.0
0.0 1.9 -0.0 -0.0
9.2
9.2
X
Y
(m)
(m)
549215.98 4813578.85
549222.80 4813567.67
Z
(m)
2.00
0
0 72.5 72.5 0.0 0.0 62.2 1.7 0.2 0.0
0.0 13.0 -0.0 -0.0 -4.6 -4.6
2.00
0
0 81.5 81.5 0.0 0.0 61.9 1.7 0.2 0.0
0.0 13.8 -0.0 -0.0
3.9
3.9
Page5
Receiver
Name:
Vacant Lot located west side of the facility
ID: POR7
X:
549101.65
Y:
4813395.86
Z:
4.50
Nr.
1
Nr.
1
Nr.
1
Nr.
1
Nr.
1
Nr.
1
Nr.
1
Nr.
1
X
Y
(m)
(m)
549190.22 4813535.76
Point Source, ISO 9613, Name: ''Air Intake'', ID: ''AIR1''
Z
(m)
15.36
0
0 81.8 81.8 0.0 0.0 55.4 0.9 -0.8 0.0
0.0 0.0 -0.0 -0.0 26.3 26.3
X
Y
(m)
(m)
549154.56 4813493.49
Point Source, ISO 9613, Name: ''Barn Fan '', ID: ''BF''
Z
(m)
4.00
0
0 85.4 85.4 0.0 0.0 51.9 0.8 -0.8 0.0
0.0 0.0 -0.0 -0.0 33.4 33.4
X
Y
(m)
(m)
549245.25 4813529.14
Point Source, ISO 9613, Name: ''Condensing unit 11'', ID: ''CU11''
Z
(m)
9.00
0
0 86.2 86.2 0.0 0.0 56.8 0.5 -0.3 0.0
0.0 4.6 -0.0 -0.0 24.5 24.5
X
Y
(m)
(m)
549265.93 4813560.22
Point Source, ISO 9613, Name: ''Condensing Unit 12&13'', ID: ''CU12''
Z
(m)
12.00
0
0 79.4 79.4 0.0 0.0 58.3 1.2 -0.6 0.0
0.0 0.0 -0.0 -0.0 20.5 20.5
X
Y
(m)
(m)
549275.49 4813518.12
Z
(m)
9.00
0
0 83.0 83.0 0.0 0.0 57.5 0.6 -0.3 0.0
0.0 2.1 -0.0 -0.0 23.0 23.0
X
Y
(m)
(m)
549272.44 4813501.84
Z
(m)
9.00
0
0 85.3 85.3 0.0 0.0 57.1 0.6 -0.3 0.0
0.0 4.6 -0.0 -0.0 23.4 23.4
X
Y
(m)
(m)
549246.30 4813494.60
Z
(m)
10.00
0
0 81.8 81.8 0.0 0.0 55.9 1.0 -0.7 0.0
0.0 0.0 -0.0 -0.0 25.6 25.6
X
Y
(m)
(m)
549211.32 4813440.01
Point Source, ISO 9613, Name: ''Condnsing Unit 24-Top'', ID: ''CU24''
Z
(m)
12.10
0
0 93.8 93.8 0.0 0.0 52.5 1.3 -0.7 0.0
0.0 4.8 -0.0 -0.0 36.0 36.0
Page6
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1
Nr.
1
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1
Nr.
1
Nr.
1
Nr.
1
Nr.
1
Nr.
1
Nr.
1
X
Y
Z
(m)
(m)
(m)
549208.94 4813438.82
9.50
0
0 91.2 91.2 3.0 0.0 52.3 1.5 -0.7 0.0
0.0 0.0 -0.0 -0.0 41.1 41.1
X
Y
Z
(m)
(m)
(m)
549212.04 4813438.63
9.50
0
0 91.2 91.2 3.0 0.0 52.5 1.5 -0.6 0.0
0.0 4.9 -0.0 -0.0 35.9 35.9
X
Y
Z
(m)
(m)
(m)
549213.95 4813441.26
9.50
0
0 91.2 91.2 3.0 0.0 52.7 1.5 -0.3 0.0
0.0 13.3 -0.0 -0.0 26.9 26.9
X
Y
Z
(m)
(m)
(m)
549210.74 4813441.37
9.50
0
0 91.2 91.2 3.0 0.0 52.5 1.5 -0.7 0.0
0.0 0.0 -0.0 -0.0 40.9 40.9
X
Y
(m)
(m)
549217.02 4813442.69
Z
(m)
12.10
0
0 93.8 93.8 0.0 0.0 52.9 1.4 -0.6 0.0
0.0 4.1 -0.0 -0.0 36.0 36.0
X
Y
Z
(m)
(m)
(m)
549214.42 4813441.56
9.50
0
0 91.2 91.2 3.0 0.0 52.7 1.5 -0.3 0.0
0.0 12.0 -0.0 -0.0 28.2 28.2
X
Y
Z
(m)
(m)
(m)
549217.72 4813441.29
9.50
0
0 91.2 91.2 3.0 0.0 52.9 1.6 -0.6 0.0
0.0 5.8 -0.0 -0.0 34.5 34.5
X
Y
Z
(m)
(m)
(m)
549219.81 4813443.97
9.50
0
0 91.2 91.2 3.0 0.0 53.1 1.6 -0.3 0.0
0.0 13.4 -0.0 -0.0 26.4 26.4
X
Y
Z
(m)
(m)
(m)
549216.48 4813444.06
9.50
0
0 91.2 91.2 3.0 0.0 52.9 1.6 -0.7 0.0
0.0 0.0 -0.0 -0.0 40.4 40.4
X
Y
(m)
(m)
549220.25 4813435.74
Z
(m)
12.10
0
0 93.8 93.8 0.0 0.0 53.0 1.4 -0.7 0.0
0.0 4.7 -0.0 -0.0 35.4 35.4
Page7
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1
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1
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1
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1
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1
Nr.
1
Nr.
1
Nr.
1
X
Y
Z
(m)
(m)
(m)
549217.94 4813434.70
9.50
0
0 91.2 91.2 3.0 0.0 52.8 1.5 -0.7 0.0
0.0 0.0 -0.0 -0.0 40.5 40.5
X
Y
Z
(m)
(m)
(m)
549220.85 4813434.33
9.50
0
0 91.2 91.2 3.0 0.0 53.0 1.6 -0.6 0.0
0.0 5.6 -0.0 -0.0 34.6 34.6
X
Y
Z
(m)
(m)
(m)
549222.93 4813437.08
9.50
0
0 91.2 91.2 3.0 0.0 53.2 1.6 -0.3 0.0
0.0 13.3 -0.0 -0.0 26.4 26.4
X
Y
Z
(m)
(m)
(m)
549219.61 4813437.11
9.50
0
0 91.2 91.2 3.0 0.0 52.9 1.6 -0.7 0.0
0.0 0.0 -0.0 -0.0 40.3 40.3
X
Y
(m)
(m)
549230.95 4813502.12
Z
(m)
6.70
0
0 90.8 90.8 0.0 0.0 55.5 0.5 -0.7 0.0
0.0 0.0 -0.0 -0.0 35.4 35.4
X
Y
(m)
(m)
549232.42 4813497.57
Z
(m)
6.70
0
0 90.8 90.8 0.0 0.0 55.4 0.5 -0.7 0.0
0.0 0.0 -0.0 -0.0 35.5 35.5
X
Y
(m)
(m)
549234.69 4813492.22
Z
(m)
6.70
0
0 90.8 90.8 0.0 0.0 55.3 0.5 -0.7 0.0
0.0 0.0 -0.0 -0.0 35.6 35.6
X
Y
(m)
(m)
549220.28 4813518.22
Point Source, ISO 9613, Name: ''Condensing Unit 5&6&7'', ID: ''CU5''
Z
(m)
9.00
0
0 90.7 90.7 0.0 0.0 55.6 0.9 -0.6 0.0
0.0 4.6 -0.0 -0.0 30.1 30.1
X
Y
(m)
(m)
549188.96 4813537.86
Point Source, ISO 9613, Name: ''Quickwater boiler exhaust'', ID: ''ES4''
Z
(m)
17.30
0
0 80.9 80.9 0.0 0.0 55.5 0.4 -0.3 0.0
0.0 0.0 -0.0 -0.0 25.3 25.3
X
Y
(m)
(m)
549136.23 4813509.80
Point Source, ISO 9613, Name: ''Hogs Noise'', ID: ''HN''
Z
(m)
2.00
0
0 85.6 85.6 0.0 0.0 52.5 0.5 -0.5 0.0
0.0 0.0 -0.0 -0.0 33.0 33.0
Page8
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1
Nr.
1
Nr.
1
Nr.
1
Nr.
1
Nr.
1
Nr.
1
Nr.
1
Nr.
1
Nr.
1
X
Y
(m)
(m)
549151.79 4813497.12
Point Source, ISO 9613, Name: ''Truck unloading hogs'', ID: ''HT''
Z
(m)
2.00
0
0 94.4 94.4 0.0 0.0 52.1 0.9 -0.6 0.0
0.0 0.0 -0.0 -0.0 42.0 42.0
X
Y
(m)
(m)
549373.25 4813530.25
Point Source, ISO 9613, Name: ''Blower Louver'', ID: ''LV1''
Z
(m)
3.66
0
0 94.7 94.7 0.0 0.0 60.6 1.5 -1.0 0.0
0.0 6.4 -0.0 -0.0 27.3 27.3
X
Y
(m)
(m)
549208.69 4813432.66
Z
(m)
1.50
0
0 84.8 84.8 0.0 0.0 52.1 0.5 0.9 0.0
0.0 0.0 -0.0 -0.0 31.3 31.3
X
Y
(m)
(m)
549206.79 4813436.73
Z
(m)
3.66
0
0 84.8 84.8 0.0 0.0 52.0 0.5 -0.7 0.0
0.0 0.0 -0.0 -0.0 33.0 33.0
X
Y
(m)
(m)
549205.10 4813440.45
Z
(m)
5.00
0
0 84.8 84.8 0.0 0.0 52.0 0.5 -0.8 0.0
0.0 0.0 -0.0 -0.0 33.1 33.1
X
Y
(m)
(m)
549225.57 4813552.57
Z
(m)
4.00
0
0 85.8 85.8 0.0 0.0 57.0 1.0 1.1 0.0
0.0 12.1 -0.0 -0.0 14.7 14.7
X
Y
(m)
(m)
549229.19 4813554.78
Z
(m)
4.00
0
0 85.8 85.8 0.0 0.0 57.2 1.0 1.1 0.0
0.0 11.1 -0.0 -0.0 15.4 15.4
X
Y
(m)
(m)
549232.36 4813556.62
Z
(m)
4.00
0
0 85.8 85.8 0.0 0.0 57.3 1.0 1.1 0.0
0.0 10.4 -0.0 -0.0 15.9 15.9
X
Y
(m)
(m)
549235.96 4813558.54
Z
(m)
4.00
0
0 85.8 85.8 0.0 0.0 57.5 1.0 1.1 0.0
0.0 9.8 -0.0 -0.0 16.3 16.3
X
Y
(m)
(m)
549240.10 4813560.37
Z
(m)
4.00
0
0 85.8 85.8 0.0 0.0 57.6 1.0 1.1 0.0
0.0 10.5 -0.0 -0.0 15.5 15.5
Page9
Nr.
1
Nr.
1
Nr.
1
Nr.
1
Nr.
1
Nr.
1
Nr.
1
Nr.
1
2
Nr.
1
X
Y
(m)
(m)
549243.45 4813562.33
Z
(m)
4.00
0
0 85.8 85.8 0.0 0.0 57.8 1.0 1.1 0.0
0.0 10.1 -0.0 -0.0 15.7 15.7
X
Y
(m)
(m)
549246.30 4813563.67
Z
(m)
4.00
0
0 85.8 85.8 0.0 0.0 57.9 1.0 1.1 0.0
0.0 9.7 -0.0 -0.0 15.9 15.9
X
Y
(m)
(m)
549323.89 4813585.08
Z
(m)
4.00
0
0 85.8 85.8 0.0 0.0 60.3 1.3 0.8 0.0
0.0 6.1 -0.0 -0.0 17.2 17.2
X
Y
(m)
(m)
549295.33 4813516.61
Z
(m)
4.00
0
0 85.8 85.8 0.0 0.0 58.2 1.1 1.0 0.0
0.0 17.0 -0.0 -0.0
8.5
8.5
X
Y
(m)
(m)
549141.82 4813532.08
Point Source, ISO 9613, Name: ''make up air unit 21'', ID: ''RTU21''
Z
(m)
4.00
0
0 78.3 78.3 0.0 0.0 54.0 0.9 -0.8 0.0
0.0 0.0 -0.0 -0.0 24.2 24.2
X
Y
(m)
(m)
549150.85 4813539.43
Point Source, ISO 9613, Name: ''Air make up unit 22'', ID: ''RTU22''
Z
(m)
4.00
0
0 78.3 78.3 0.0 0.0 54.6 0.9 -1.0 0.0
0.0 13.5 -0.0 -0.0 10.2 10.2
X
Y
(m)
(m)
549364.70 4813559.58
Point Source, ISO 9613, Name: ''Sludge Tanks'', ID: ''ST''
Z
(m)
0.00
0
0 77.6 77.6 0.0 0.0 60.8 1.6 5.0 0.0
0.0 7.3 -0.0 -0.0
2.9
2.9
X
Y
(m)
(m)
549113.77 4813492.73
549139.91 4813494.85
Z
(m)
2.00
0
0 80.1 80.1 0.0 0.0 50.8 0.6 -0.5 0.0
0.0 0.0 -0.0 -0.0 29.2 29.2
2.00
0
0 77.4 77.4 0.0 0.0 51.5 0.6 -0.4 0.0
0.0 0.0 -0.0 -0.0 25.7 25.7
X
Y
(m)
(m)
549222.04 4813568.92
Z
(m)
2.00
0
0 82.0 82.0 0.0 0.0 57.5 1.1 0.4 0.0
0.0 15.9 -0.0 -0.0
7.1
7.1
Page10

CONESTOGA MEAT PACKERS LIMITED BRESLAU, ONTARIO

Transcription

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