IN THE MATTER OF:
PROPOSED NEW AND UPDATED RULES FOR MEASUREMENT AND NUMERICAL SOUND EMISSIONS STANDARDS AMENDMENTS TO 35 ILL. ADM CODE 901 and 910 |
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R03-9 (Rulemaking - Noise) |
The Board held two hearings before Board Hearing Officer Marie Tipsord. The third hearing (Tr.3) was held February 10, 2004, in Chicago. At that hearing, Mr. John P. McGillivray testified on behalf of Scot-Forge Company and Howard Chinn testified on behalf of the AGO. The fourth hearing (Tr.4) was held November 4, 2004, in Springfield. Mr. John Henriksen and Dane Tittman testified on behalf of the IAAP. | |
The Board received six additional comments during the second phase of hearings. The comments were from Moline Forge (PC 8), Intermet (PC 9,) IAAP (PC 10), the AGO (PC 11), Village of Bridgeview (Bridgeview) (PC 12), and the Illinois Department of Natural Resources (IDNR) (PC 13). | |
On March 17, 2005, the Board proceeded to a second first notice with this rulemaking. That first notice was published in the Illinois Register on April 15, 2005 (29 Ill. Reg. 5196). The Board held an additional hearing on September 1, 2005 (Tr. 5) and at that hearing Mr. Henriksen again testified along with Mr. Willard Pierce of Evenson Explosives, LLC on behalf of IAAP. Also Mr. Jim Hafliger of the IDNR testified. The public comment period closed on October 17, 2005, and the Board received six additional comments during the 2005 first-notice period. Those comments are: | |
PC 14 | Joseph R. Angleton, Office Director, Office of Mines and Minerals, Illinois Department of Natural Resources | |
PC 15 | John Henriksen, Executive Director, Illinois Association of Aggregate Producers | |
PC 16 | Dr. Paul Schomer, Schomer and Associates, Inc. | |
PC 17 | Therese M. Dorigan, Bradburne, Briller & Johnson, LLC | |
PC 18 | Village of Bridgeview | |
PC 19 | Dr. Paul Schomer, on behalf of Village of Bridgeview | |
Testimony
| |
At the September 1, 2005 hearing, Mr. John Henriksen again testified along with Mr. Willard Pierce of Evenson Explosives, LLC on behalf of IAAP. Also Mr. Jim Hafliger of the Illinois Department of Natural Resources (IDNR), Office of Mines and Minerals testified. | |
Mr. John Henriksen | |
Mr. Henriksen testifies that IDNR’s Office of Mines and Minerals has promulgated a comprehensive set of regulations that subjects explosives blasting at coal mining and aggregate mining operations to air blast or ground vibration monitoring, or both, as necessary to prevent property damage and protect public safety. Tr.5 at 7-8. Additionally, IDNR enforces the regulations using highly trained, technologically proficient inspectors and state of the art equipment. Id. | |
Mr. Pierce expresses concern over the inconsistency in the C-weighted numbers between those in Section 901.109 and IDNR’s rules. Tr.5 at 25-26. Mr. Pierce also suggests that there should only be one standard and that standard should not deviate depending on the time of day or the number of times a blast occurs during the day. Tr.5 at 26. | |
Mr. Pierce also testifies that an air blast is a very specific type of sound and is a very low frequency. Tr.5 at 26. Mr. Pierce states that you do not actually “hear” an air blast but rather the effects of the air blast. Id. For example, Mr. Pierce states that you may hear surface delays or venting and you might feel the blast in your chest. Id. | |
As indicated by the list above the Board received six comments including two from Dr. Paul Schomer including one on behalf of the Village of Bridgeview. The Board will group the comments by the author of the comment. | |
Office of Mines and Minerals, IDNR | |
IDNR regulates blasting operations at all surface aggregate and coal mines in Illinois. PC 14 at 1. IDNR’s comprehensive regulations help prevent personal injury and property damage though the use of the conservative limits of one inch per second ground vibration and 133dB maximum air over pressure. Id. IDNR comments that these standards are nationally recognized and accepted industry practice. Id. IDNR determines regulatory compliance by routinely inspecting and monitoring blasting at all of the State’s 172 active aggregate and coal blasting sites. Id. IDNR’s staff of 13 people have over 100 years of combined explosives related experience and field inspectors trained in the technical elements of seismology regularly monitor blasting using state-of-the-art seismographs. Id. | |
IDNR specifically lists several points where the Board’s proposal is inconsistent or deviates from IDNR’s standards and IDNR recommends changes for consistency. First, IDNR notes that the amendments to Section 901.109(a) result in limits that are inconsistent with and less stringent than the IDNR limits. PC 14 at 1. IDNR also suggests that the limits remain constant from sunrise to sunset and not be amended based on the time of day. PC 14 at 2. IDNR recommends that the regulatory limits apply to the nearest protected structure rather than the property line. Id. IDNR also notes that the monitoring methods in Part 910 are not conducive for use in monitoring blasting and seismographs are specifically designed for monitoring blasting. Id. | |
IDNR states that the proposed rules are trying to fit air over pressure within the scope of intrusive noise and sound regulations when in fact the two are separate issues. PC 14 at 2. IDNR suggests that the surface aggregate and coal mine blasting provisions in the Board’s rules be deferred to IDNR for regulation. Id. | |
IAAP | |
IAAP’s public comment echoes the testimony of Mr. Henriksen in suggesting that the Board can and should defer to IDNR for the regulation of blasting at aggregate and coal mining operations. PC 15. IAAP points out that IDNR has regulated blasting operations at aggregate mines since 1995 and surface coal mines since 1982. Id. IAAP suggests that if the Board does decide to regulate blasting from mine operations, then the rules should be amended to ensure consistency between the Board and IDNR’s regulations. Id. | |
Ms. Therese M. Dorigan | |
Ms. Dorigan filed a comment on behalf of Kropp Forge. PC 17. Ms. Dorigan notes that Kropp Forge is not seeking any site-specific relief in this proceeding, but wishes to preserve any right to seek site-specific relief from the Board at a future date. Id. | |
Dr. Paul Schomer and Village of Bridgeview | |
1. | A lay person does not understand or necessarily hear properly background noise; |
2. | A lay person does not understand the role that wind induced noise makes on measurements; |
3. | A lay person does not understand the role that reflecting surfaces have on noise measurements. PC 16 at 2-3. |
The “implications” of errors in measurement in Dr. Schomer’s opinion is that the evidence of noise emissions measured by a lay person is inherently unreliable. PC 16 at 3. | |
Dr. Schomer argues that the Board has a viable option in terms of identifying qualified noise professionals. PC 16 at 5. Dr. Schomer urges the Board to require that measurements of noise emissions be supervised by an individual who is a “Member, Board Certified, of the Institute of Noise Control Engineering of the USA” (Institute). Id. Dr. Schomer states that the Institute is a non-profit technical society and certification requires education, several years experience, passing a rigorous 8-hour exam, and periodic professional activities to maintain certification. Id. | |
Dr. Schomer notes that as a lessor option, the Board could require that a member of the Institute, who is also a full member of the Acoustical Society of America, supervise noise emission measurements. PC 16 at 6. Dr. Schomer opines that with such a requirement the individual supervising the measurements “has some working knowledge of the mathematics of acoustics and of acoustical measurement.” Id. | |
Efficacy of the Rules. Dr. Schomer argues that allowing a lay person to make hand held A-weighted measurements does a disservice to the rules and to the noise receiver. PC 16 at 3. Dr. Schomer states that there is a trade-off between the complexity of the rules and the efficacy of the regulations. Id. Dr. Schomer notes that the Illinois rules are more complex than in many states, but as a result, Illinois’ rules are more useful and protective. Id. Dr. Schomer asserts that because measurements made with simple, hand-held A-weighted instruments fail to address the spectrum of octaves covered under Illinois regulations, the measurements give a misleading picture of the noise emissions. PC 16 at 4. Dr. Schomer opines that to the extent the Board allows such evidence to be admitted in a nuisance noise case, the entire decision making process may be tainted by misleading information. Id. | |
Dr. Schomer, in his comment filed for Bridgeview, asserts that poor instruments may not detect many valid nuisance noise instances. PC 19 at 2. The instruments that do not measure individual octave bands may result in missing noise at a low frequency, according to Dr. Schomer. Id. Dr. Schomer argues that the octave band nature of the Board’s rules is a positive factor and should not be “squandered” by substituting A-weighted measurements of questionable validity. Id. | |
Nuisance Noise Cases. Bridgeview argues the Board should take the opportunity in these rules to establish that in a nuisance complaint valid noise measurements must be used. PC 18 at 1. Bridgeview states that if noise measurements are taken in a nuisance case, the measurements should be taken as directed in Part 910. Id. Bridgeview maintains that to do otherwise is misleading to the complainant, prejudicial to the Board’s decisions, and fundamentally unfair and costly to respondents. Id. | |
Bridgeview argues that admitting noise emissions measurements taken by a lay person other than pursuant to the requirements of Part 910 is contrary to the Board’s responsibility for admitting scientific evidence based on Daubert v. Merrell Dow Pharmaceuticals, Inc., 501 U.S. 579 (1993). PC 18 at 2. Bridgeview asserts that the Board recognizes the legal principal articulated in Daubert but retreats froM the sound science approach in nuisance cases. Id. Bridgeview opines that allowing “quick and dirty” sound measurements to be used in nuisance cases, the Board is encouraging frivolous lawsuits. Id. Bridgeview further argues that the Board appears to be shifting the burden of proof by requiring the respondent to expose problems with the measurements. PC 18 at 3. | |
During the first-notice period, the comments and testimony received by the Board reiterated issues raised prior to the Board proceeding to first notice in March 2005. The issues are: (1) whether blasting operations by aggregate producers and surface coal mines should be governed by rules adopted by the Board or should the Board defer to IDNR’s regulations; and (2) whether the Board should require that noise measurements taken for presentation in a nuisance noise enforcement case should be taken pursuant to 35 Ill. Adm. Code 910. The Board will address these issues below. | |
Applicability of Noise Rules to Aggregate Producers and Surface Coal Mines | |
At first notice, the Board did make changes to the rule in response to IAAP’s comments. After consideration of the testimony and comments from IAAP and IDNR during the first-notice comment period, the Board is convinced that additional changes to the rule are warranted. | |
The testimony of IAAP and IDNR clearly demonstrates that IDNR has an extensive regulatory program in place that regulates the noise from blasting at facilities operated by aggregate producers and surface coal mines. Further, IDNR has an active staff that regularly oversees blasting and monitoring of the blasting at sites in Illinois. IDNR also has stringent enforcement tools for any violation of the regulations when blasting. Therefore, the Board finds that the Board can appropriately defer the regulation of noise emissions from blasting at aggregate and surface coal mines to IDNR. The Board will make changes to the rule under Sections 901.107 and 901.109 to reflect that deference. | |
The Board notes that IAAP’s testimony indicates that IAAP only asks the Board to defer to IDNR for blasting at the aggregate producers sites in Illinois. All other operations, such as back up beepers, ingress and egress, and daily production noise emission should be subject to the Board rules according to IAAP. In light of this, the Board limits the scope of the proposed exemption to only to impulsive sound produced by explosive blasting activities, which are regulated by IDNR in accordance with Section 6.5 and Section 3.13 of the Surface Coal Mining Land Conservation and Reclamation Act (225 ILCS 715/6.5 and 3.13 (2004)). | |
Applicability of Part 910 to Nuisance Noise Enforcement Cases | |
The Board has long held in that noise measurements may be used to substantiate or refute a nuisance noise claim. See Discovery South Group v. PCB, 275 Ill. App. 3d 547, 549, 656 N.E.2d 51, 59 (1st Dist. 1995); Charter Hall Home Owners Association v. Overland Transportation System PCB 98-81 (Oct. 1, 1998); Pawlowski v. Benchwarmers Pub, PCB 99-82 (Apr. 6, 2000); Gladys Knox and David Knox v. Turris Coal Company and AEI Resources, Inc., PCB 00-140 (Jan. 9, 2003). In the Board’s first-notice opinion and order, the Board stated: | |
Section 910.104 clarifies that sound pressure level measurements are not required to establish a violation of the Board’s nuisance noise standard at Section 900.102, although such measurements may be used as corroborating evidence. In light of this, the Board finds that compliance with the detailed sound measurement procedures set forth in Part 951 or the proposed Part 910 are not required for sound measurements used as corroborating evidence in a nuisance noise proceeding. The Board will assign appropriate weight to sound measurement data submitted in any nuisance noise complaint based on the information in the hearing record and in accordance with the provisions of the Act. As noted in the first first-notice opinion (Proposed New and Updated Rules for Measurement and Numerical Sound Emissions Standards; Amendments to 35 Ill. Adm. Code 901 and 910, R03-9 (July 10, 1003)), the Board believes that this approach is consistent with the Board’s precedence and case law concerning nuisance noise complaints. The Board declines to make the changes suggested by IAAP. Proposed New and Updated Rules for Measurement and Numerical Sound Emissions Standards; Amendments to 35 Ill. Adm. Code 901 and 910, R03-9, (Mar. 17, 2005). | |
The Board also discussed, at first notice, the request that noise measurements be supervised by an individual who is certified. The Board stated: | |
The Board finds that the present regulatory structure, where the Board determines the validity of sound data on a case-by-case basis in noise enforcement cases, is a more prudent approach than prescribing vague qualification requirements. The Board believes this is especially true absent a State approved licensing or certification process. Proposed New and Updated Rules for Measurement and Numerical Sound Emissions Standards; Amendments to 35 Ill. Adm. Code 901 and 910, R03-9, (Mar. 17, 2005). | |
The Board has carefully reviewed the arguments and concerns expressed by Bridgeview and Dr. Schomer. However, the Board is unconvinced that a change to the rule is necessary. First, as to the suggestion that the Board require compliance with Part 910 for measurement of noise emissions in a nuisance noise enforcement, the Board does not believe that change is necessary. If a complainant complies with the requirements of Part 910 when alleging a violation, then such a violation would be of the numeric standards and not a nuisance violation. The Board has long heard testimony in nuisance noise enforcement cases concerning the use of noise measurements. The Board examines that testimony and the measurements in light of the entirety of the evidence and renders a decision as to whether the noise unreasonablY interferes with the enjoyment of life. See e.g., Zivoli v. Somebody’s Bar and Restaurant, PCB 90-200 (May 21, 1992). Therefore, the Board declines to make a change to the rule. | |
regarding the qualifications of individual supervising the measurement of emissions, the Board is not persuaded that requiring certification by the Institute is appropriate. The Board will continue to review the noise emission measurements on a case-by-case basis and make determination based on the evidence provided. | |
The Board finds that the extensive record in this proceeding supports proceeding to second notice with these noise regulations. The Board further finds that the rules are technically feasible and economically reasonable. Therefore the Board will proceed to second notice. | |
The Board today adopts for second notice regulations concerning measurement of and standards for noise emissions in Illinois. The Board defers regulation of blasting operations at aggregate and surface coal mines to IDNR, who has an extensive regulatory scheme in place. The Board declines to alter the Board’s longstanding position on noise emission measurements in nuisance noise enforcement cases and to require measurements be supervised by a certified individual. The Board sends this proceeding to the Joint Committee on Administrative Review for second notice consideration. | |
901.101 | Classification of Land According to Use |
901.102 | Sound Emitted to Class A Land |
901.103 | Sound Emitted to Class B Land |
901.104 | Highly - Impulsive Sound |
901.105 | Impact Forging Operations |
901.106 | Prominent Discrete Tones |
901.107 | Exceptions |
901.108 | Compliance Dates for Part 901 |
901.109 | Highly - Impulsive Sound from Explosive Blasting |
901.110 | Amforge Operational Level |
901.111 | Modern Drop Forge Operational Level |
901.112 | Wyman-Gordon Operational Level |
901.113 | Wagner Casting Site-Specific Operational Level (Repealed) |
901.114 | Moline Forge Operational Level |
901.115 | Cornell Forge Hampshire Division Site-Specific Operational Level |
901.116 | Forgings and Stampings, Inc. Operational Level |
901.117 | Rockford Drop Forge Company Operational Level |
901.118 | |
901.119 | Clifford-Jacobs Operational Level |
901.120 | C.S. Norcross Operational Level |
901.121 | Vaughan & Bushnell Operational Level |
APPENDIX A | Old Rule Numbers Referenced |
APPENDIX B | Land-Based Classification Standards |
a) | The land use classification system used for the purposes of applying numeric sound standards for this Part is based on the Land-Based Classification Standards (LBCS) (Jeer, Sanjay. 2001. Land-Based Classification Standards . Online, http://www.planning.org/LBCS . American Planning Association: Chicago, Illinois). The LBCS applicable to this Part is set forth in Appendix B. |
b) | Class A land includes |
c) | Class B land includes |
d) | Class C land includes |
e) | A parcel or tract of land used as specified by LBCS |
a) | Except as elsewhere provided in this Part |
Octave Band Center Frequency (Hertz)
|
Allowable Octave Band Sound Pressure Levels (dB) of Sound Emitted to any Receiving Class A Land from
|
Class C Land
|
Class B Land
|
Class A Land
|
|
31.5
|
75
|
72
|
72
|
63
|
74
|
71
|
71
|
125
|
69
|
65
|
65
|
250
|
64
|
57
|
57
|
500
|
58
|
51
|
51
|
1000
|
52
|
45
|
45
|
2000
|
47
|
39
|
39
|
4000
|
43
|
34
|
34
|
8000
|
40
|
32
|
32
|
b) | Except as provided elsewhere in this Part |
Octave Band Center Frequency (Hertz)
|
Allowable Octave Band Sound Pressure Levels (dB) of Sound Emitted to any Receiving Class A Land from
|
Class C Land
|
Class B Land
|
Class A Land
|
|
31.5
|
69
|
63
|
63
|
63
|
67
|
61
|
61
|
125
|
62
|
55
|
55
|
250
|
54
|
47
|
47
|
500
|
47
|
40
|
40
|
1000
|
41
|
35
|
35
|
2000
|
36
|
30
|
30
|
4000
|
32
|
25
|
25
|
8000
|
32
|
25
|
25
|
Octave Band Center Frequency (Hertz)
|
Allowable Octave Band Sound Pressure Levels (dB) of Sound Emitted to any Receiving Class B Land from
|
Class C Land
|
Class B Land
|
Class A Land
|
|
31.5
|
80
|
79
|
72
|
63
|
79
|
78
|
71
|
125
|
74
|
72
|
65
|
250
|
69
|
64
|
57
|
500
|
63
|
58
|
51
|
1000
|
57
|
52
|
45
|
2000
|
52
|
46
|
39
|
4000
|
48
|
41
|
34
|
8000
|
45
|
39
|
32
|
Classification of Land on which Property-Line Noise-Source: is Located
|
Allowable A-weighted Sound Levels in Decibels of Highly-Impulsive Sound Emitted to Receiving Class A or B Land
|
Class B Land | Class A Land | ||
Daytime | Nighttime | ||
Class A Land | |||
Class B Land | |||
Class C Land |
1) | Daytime hours means |
2) | Nighttime hours means |
3) | The reference time for Leq, as defined in 35 Ill. Adm. Code 900.101 is one hour. |
4) | New Impacting Forging Operation is that property-line-noise-source comprised of impact forging operation on which construction began after September 1, 1982. |
5) | Existing Impact Forging Operation is that property-line-noise-source comprised of impact forging operations which are in existence on September 1, 1982, |
b) | Emission Limitations for New Impact Forging Operation. |
Class B Land
|
Class A Land
|
Daytime
|
Nighttime
|
|
59.5
|
53.5
|
48.5
|
c) | Limitations for Existing Impact Forging Operation | |
Class B Land
|
Class A Land
|
Daytime
|
Nighttime
|
|
64.5
|
58.5
|
53.5
|
d) | Site Specific Allowable Operational Level for Existing Impact Forging Operation |
1) | An existing impact forging operation which does not comply with subsection |
2) | Any existing impact forging operation seeking a permanent site specific operational level must submit as its petition the following: |
A) | The location of the petitioner, a description of the surrounding community, and a map locating the petitioner within the community; |
B) | A description of the petitioner's operations, the number and size of the petitioner's forging hammers, the current hours of hammer operation, the approximate number of forgings manufactured during each of the three prior calendar years and the approximate number of hammer blows used to manufacture the forgings. |
D) | The sound levels in excess of those permitted by subsection |
E) | The number of residences exposed to sound levels in excess of those permitted by subsection |
F) | A description of other significant sources of noise (mobile and stationary) and their location shown on the map of the community; |
G) | A description of the proposed operational level and proposed physical abatement measures, if any, a schedule for their implementation and their costs; |
H) | The predicted improvement in community sound levels as a result of implementation of the proposed abatement measures; and |
I) | A description of the economic and technical considerations which justify the permanent site specific allowable operational level sought by petitioner. |
f) | Site-Specific Operational Levels |
a) | No person shall cause or allow the emission of any prominent discrete tone from any property-line-noise-source located on any Class A, B or C land to any receiving Class A, B or C land, provided, however, that no measurement of one-third octave band sound pressure levels shall be made less than 25 feet from such property-line source. |
b) | This rule shall not apply to prominent discrete tones having a one-third octave band sound pressure level 10 or more dB below the allowable octave band sound pressure level specified in |
a) | Sections 901.102 through 901.106 inclusive does |
b) | Sections 901.102 through 901.106 inclusive does |
c) | Sections 901.102 through 901.106 inclusive does |
d) | Sections 901.102 through 901.106 inclusive do |
e) | Section 901.102(b) do |
f) | Sections 901.102 through 901.106 inclusive do |
g) | Sections 901.102 through 901.106 inclusive do |
h) | Section 901.104 shall not apply to impulsive sound produced by explosive blasting activities conducted on any Class C land other than the land used as specified by LBCS Codes 8300 and 8500 |
i) | Part 901 shall not apply to impulsive sound produced by explosive blasting activities, which are: |
1) | Conducted on any Class C land used as specified by LBCS Codes 8300 and 8500; and |
2) | Regulated by the Department of Natural Resources in accordance with Section 6.5 and Section 3.13 of the Surface Coal Mining Land Conservation and Reclamation Act (225 ILCS 715/6.5 and 3.13 (2004)). |
j | Sections 901.102 through 901.106 inclusive |
a) | Except as provided in subsections |
b) | Except as otherwise provided in this rule, every owner or operator of an existing property-line-noise-source must |
c) | Every owner or operator of an existing property-line-noise-source who emits sound which exceeds any allowable octave band sound pressure level of Section 901.102 or 901.103 by 10 dB or more in any octave band with a center frequency of 31.5 Hertz, 63 Hertz or 125 Hertz must |
d) | Except as provided in subsections |
e) | Every owner or operator of an existing property-line-noise-source required to comply with Section 901.106 must |
f) | Every owner or operator of Class C land now and hereafter used as specified by LBCS Code 4120 |
g) | Existing impact forging operations as defined in Section 901.105 which do not seek permanent site specific allowable operational levels must |
h) | Every owner or operator of Class C land now or hereafter used as specified by LBCS Code 3310 |
i) | Every owner or operator of Class C land now or hereafter used as specified by LBCS Code 5130 and 5140 |
a) | During the daytime hours that cover the period |
Receiving Class A Land
|
Receiving Class B Land
|
b) | Compliance with outdoor peak sound pressure level limits in the following table shall constitute prima facie level limits of this rule when measured on such receiving Class A or B land. |
Lower Frequency Limit of Measuring System for Flat Response, a Variation from Linear Response of + or - 3dB (Hz) | Receiving Class A Land (dB)
|
Receiving Class B Land (dB)
|
< 2.0 but > 0.1 | 133
|
133
|
c) | During the period defined by both the beginning of the nighttime hours (10:00 pm) or sunset, whichever occurs earlier and the ending of the nighttime hours (7:00 am) or , |
d) | Persons causing or allowing explosive blasting to be conducted on any Class C land other than land used as specified by LBCS Code 8300 or 8500 |
b) | Operation of its forging hammers is limited to the hours of 7:00 a.m. through 11:00 p.m., with occasional operations beginning at 6:00 a.m. and ending at midnight, Monday through Saturdays; and |
c) | Install sound |
b) | Operate its forging hammers only during the hours of 6:00 a.m. through midnight, Mondays through Fridays, and 6:30 a.m. until 7:30 p.m. on Saturdays. |
b) | Operate its forging hammers only between the hours of 6:00 a.m. and 6:00 p.m. Monday through Saturday. |
b) | Operate its forging hammers only between the hours of 6:00 a.m. and 1:30 a.m. |
LBCS
|
Main Category
|
Function Code
|
Description | 35 IAC 901 Land Class
|
|
Residence or accommodation functions
|
1000 | Residence or accommodation functions | A
|
|
1100 | Private household | |||
1200 | Housing services for the elderly |
|
||
1210
|
Retirement housing services | ½
|
||
1220
|
Congregate living services | ½
|
||
1230
|
Assisted-living services | ½
|
||
1240
|
Life care or continuing care services | ½
|
||
1250
|
Skilled-nursing services | ½
|
||
1300 | Hotels, motels, or other accommodation services | ½
|
||
1310
|
Bed and breakfast inn | ½
|
||
1320
|
Rooming and boarding | ¯
|
||
1330
|
Hotel, motel, or tourist court | |||
1340
|
Casino hotel
|
A
|
||
General sales or services
|
2000 | General sales or services | ||
2100 | Retail sales or service | B
|
||
2110
|
Automobile sales or service establishment | |||
2111
|
Car dealer |
|
||
2112
|
Bus, truck, mobile homes, or large vehicles | ½
|
||
2113
|
Bicycle, motorcycle, ATV, etc. | ½
|
||
2114
|
Boat or marine craft dealer | ½
|
||
2115
|
Parts, accessories, or tires | ½
|
||
2116
|
Gasoline service | ½
|
||
2120
|
Heavy consumer goods sales or service | ½
|
||
2121
|
Furniture or home furnishings | ½
|
||
2122
|
Hardware, home centers, etc. | ½
|
||
2123
|
Lawn and garden supplies | ½
|
||
2124
|
Department store, warehouse club or superstore | ½
|
||
2125
|
Electronics and Appliances | ½
|
||
2126
|
Lumber yard and building materials | ½
|
||
2127
|
Heating and plumbing equipment | ½
|
||
2130
|
Durable consumer goods sales and service | ½
|
||
2131
|
Computer and software | ½
|
||
2132
|
Camera and photographic supplies | ½
|
||
2133
|
Clothing, jewelry, luggage, shoes, etc. | ½
|
||
2134
|
Sporting goods, toy and hobby, and musical instruments | ½
|
||
2135
|
Books, magazines, music, stationery | ½
|
||
2140
|
Consumer goods, other | ½
|
||
2141
|
Florist | ½
|
||
2142
|
Art dealers, supplies, sales and service | ½
|
||
2143
|
Tobacco or tobacconist establishment | ½
|
||
2144
|
Mail order or direct selling establishment | ½
|
||
2145
|
Antique shops, flea markets, etc. | ½
|
||
2150
|
Grocery, food, beverage, dairy, etc. | ½
|
||
2151
|
Grocery store, supermarket, or bakery | ½
|
||
2152
|
Convenience store | ½
|
||
2153
|
Specialty food store | ½
|
||
2154
|
Fruit and vegetable store | ½
|
||
2155
|
Beer, wine, and liquor store | ½
|
||
2160
|
Health and personal care | ½
|
||
2161
|
Pharmacy or drug store | ½
|
||
2162
|
Cosmetic and beauty supplies | ½
|
||
2163
|
Optical | ½
|
||
2200 | Finance and Insurance | ½
|
||
2210
|
Bank, credit union, or savings institution | ½
|
||
2220
|
Credit and finance establishment | ½
|
||
2230
|
Investment banking, securities, and brokerages | ½
|
||
2240
|
Insurance-related establishment | ½
|
||
2250
|
Fund, trust, or other financial establishment | ½
|
||
2300 | Real estate, and rental and leasing | ½
|
||
2310
|
Real estate services | ½
|
||
2320
|
Property management services | ½
|
||
2321
|
Commercial property-related | ½
|
||
2322
|
Rental housing-related | ½
|
||
2330
|
Rental and leasing | ½
|
||
2331
|
Cars | ½
|
||
2332
|
Leasing trucks, trailers, RVs, etc. | ½
|
||
2333
|
Recreational goods rental | ½
|
||
2334
|
Leasing commercial, industrial machinery, and equipment | ¯
|
||
2335
|
Consumer goods rental | |||
2336
|
Intellectual property rental (video, music, software, etc.) | B
|
||
2400 | Business, professional, scientific, and technical services | |||
2410
|
Professional services | A
|
||
2411
|
Legal services | |||
2412
|
Accounting, tax, bookkeeping, payroll services |
|
||
2413
|
Architectural, engineering, and related services | ½
|
||
2414
|
Graphic, industrial, interior design services | ½
|
||
2415
|
Consulting services (management, environmental, etc.) | ½
|
||
2416
|
Research and development services (scientific, etc.) | ½
|
||
2417
|
Advertising, media, and photography services | ½
|
||
2418
|
Veterinary services | ½
|
||
2420
|
Administrative services | ½
|
||
2421
|
Office and administrative services | ½
|
||
2422
|
Facilities support services | ½
|
||
2423
|
Employment agency | ½
|
||
2424
|
Business support services | ½
|
||
2425
|
Collection agency | ½
|
||
2430
|
Travel arrangement and reservation services | ½
|
||
2440
|
Investigation and security services | ½
|
||
2450
|
Services to buildings and dwellings | ½
|
||
2451
|
Extermination and pest control | ½
|
||
2452
|
Janitorial | ½
|
||
2453
|
Landscaping | ¯
|
||
2454
|
Carpet and upholstery cleaning | |||
2455
|
Packing, crating, and convention and trade show services | A
|
||
2500 | Food services | B
|
||
2510
|
Full-service restaurant | |||
2520
|
Cafeteria or limited service restaurant |
|
||
2530
|
Snack or nonalcoholic bar | ½
|
||
2540
|
Bar or drinking place | ½
|
||
2550
|
Mobile food services | ½
|
||
2560
|
Caterer | ½
|
||
2570
|
Food service contractor | ½
|
||
2580
|
Vending machine operator | ½
|
||
2600 | Personal services | ½
|
||
2700 | Pet and animal sales or service (except veterinary) | ¯
|
||
2710
|
Pet or pet supply store | |||
2720
|
Animal and pet services
|
B
|
||
Manufacturing and wholesale trade
|
3000 | Manufacturing and wholesale trade | ||
3100 | Food, textiles, and related products | C
|
||
3110
|
Food and beverages | |||
3120
|
Tobacco manufacturing establishment |
|
||
3130
|
Textiles | ½
|
||
3140
|
Leather and allied products | ½
|
||
3200 | Wood, paper, and printing products | ½
|
||
3210
|
Wood products establishment | ½
|
||
3220
|
Paper and printing materials | ½
|
||
3230
|
Furniture and related products | ½
|
||
3300 | Chemicals, and metals, machinery, and electronics manufacturing | ½
½ |
||
3310
|
Petroleum and coal products | ½
|
||
3320
|
Chemicals, plastics, and rubber products | ½
|
||
3330
|
Nonmetallic mineral products | ½
|
||
3340
|
Primary metal manufacturing | ½
|
||
3350
|
Machinery manufacturing | ½
|
||
3360
|
Electrical equipment, appliance, and components manufacturing | ½
½ |
||
3370
|
Transportation equipment, automobiles, etc. | ½
|
||
3400 | Miscellaneous manufacturing | ½
|
||
3410
|
Jewelry and silverware | ½
|
||
3420
|
Dolls, toys, games, and musical instruments | ¯
|
||
3430
|
Office supplies, inks, etc. | |||
3440
|
Signs | C
|
||
3500 | Wholesale trade establishment | B
|
||
3510
|
Durable goods |
|
||
3520
|
Nondurable goods | ¯
|
||
3600 | Warehouse and storage services
|
B
|
||
Transportation, communication, information, and utilities
|
4000 | Transportation, communication, information, and utilities | ||
4100 | Transportation services | |||
4110
|
Air transportation | U
|
||
4111
|
Air passenger transportation | |||
4112
|
Air freight transportation |
|
||
4113
|
Airport and support establishment | ¯
|
||
4114
|
Aircraft and accessories | |||
4115
|
Other air transportation (including scenic, balloon, etc.) | U
|
||
4120
|
Rail transportation | C
|
||
4121
|
Rail passenger transportation | |||
4122
|
Rail freight transportation |
|
||
4123
|
Rail transportation support establishment | ½
|
||
4130
|
Road, ground passenger, and transit transportation | ½
|
||
4131
|
Local transit systems-mixed mode | ½
|
||
4132
|
Local transit systems-commuter rail | ½
|
||
4133
|
Local transit systems-bus, special needs, and other motor vehicles | ½
½ |
||
4134
|
Interurban, charter bus, and other similar establishments | ½
|
||
4135
|
School and employee bus transportation | ½
|
||
4136
|
Special purpose transit transportation (including scenic, sightseeing, etc.) | ½
½ |
||
4137
|
Taxi and limousine service | ½
|
||
4138
|
Towing and other road and ground services | ½
|
||
4140
|
Truck and freight transportation services | ½
|
||
4141
|
General freight trucking, local | ½
|
||
4142
|
General freight trucking, long-distance | ½
|
||
4143
|
Freight trucking, specialized (used household and office goods) | ½
½ |
||
4144
|
Freight trucking, specialized (except used goods) | ½
|
||
4150
|
Marine and water transportation | ½
|
||
4151
|
Marine passenger transportation | ½
|
||
4152
|
Marine freight transportation | ½
|
||
4153
|
Marine port and harbor operations | ½
|
||
4154
|
Marine cargo handling and dry dock services | ½
|
||
4155
|
Marine navigational and other services | ½
|
||
4160
|
Courier and messenger services | ¯
|
||
4170
|
Postal services | |||
4180
|
Pipeline transportation | C
|
||
4200 | Communications and information | |||
4210
|
Publishing | C
|
||
4211
|
Newspapers, books, periodicals, etc. | C
|
||
4212
|
Software publisher | C
|
||
4220
|
Motion pictures and sound recording | B
|
||
4221
|
Motion picture and video production, publishing, and distribution | |
||
4222
|
Motion picture viewing and exhibition services | ½
|
||
4223
|
Sound recording, production, publishing, and distribution | ½
|
||
4230
|
Telecommunications and broadcasting | ½
|
||
4231
|
Radio and television broadcasting | ½
|
||
4232
|
Cable networks and distribution | ½
|
||
4233
|
Wireless telecommunications | ½
|
||
4234
|
Telephone and other wired telecommunications | ½
|
||
4240
|
Information services and data processing industries | ½
|
||
4241
|
Online information services | ¯
|
||
4242
|
Libraries and archives | |||
4243
|
News syndicate | B
|
||
4300 | Utilities and utility services | C
|
||
4310
|
Electric power | |||
4311
|
Hydroelectric |
|
||
4312
|
Fossil | ½
|
||
4313
|
Nuclear | ½
|
||
4314
|
Alternative energy sources | ½
|
||
4320
|
Natural gas, petroleum, fuels, etc. | ½
|
||
4330
|
Water, steam, air conditioning supply | ½
|
||
4331
|
Drinking water | ½
|
||
4332
|
Irrigation and industrial water supply | ½
|
||
4333
|
Air conditioning and steam supply | ½
|
||
4340
|
Sewer, solid waste, and related services | ½
|
||
4341
|
Hazardous waste collection | ½
|
||
4342
|
Hazardous waste treatment and disposal | ½
|
||
4343
|
Solid waste collection | ½
|
||
4344
|
Solid waste combustor or incinerator | ½
|
||
4345
|
Solid waste landfill | ½
|
||
4346
|
Waste treatment and disposal | ¯
|
||
4347
|
Septic tank and related services
|
C |
||
Arts, entertainment, and recreation
|
5000 | Arts, entertainment, and recreation | ||
5100 | Performing arts or supporting establishment | B
|
||
5110
|
Theater, dance, or music establishment | |||
5120
|
Sports team or club |
|
||
5130
|
Racetrack establishment | ½
|
||
5140
|
Promoter of performing arts, sports, and similar events | ¯
|
||
5150
|
Agent for management services | |||
5160
|
Independent artist, writer, or performer | B
|
||
5200 | Museums and other special purpose recreational institutions | A
|
||
5210
|
Museum |
|
||
5220
|
Historical or archeological institution | ¯
|
||
5230
|
Zoos, botanical gardens, arboreta, etc. | A
|
||
5300 | Amusement, sports, or recreation establishment | B
|
||
5310
|
Amusement or theme park establishment | |||
5320
|
Games arcade establishment |
|
||
5330
|
Casino or gambling establishment | ½
|
||
5340
|
Miniature golf establishment | ½
|
||
5350
|
Skiing | ½
|
||
5360
|
Marina or yachting club facility operators | ½
|
||
5370
|
Fitness, recreational sports, gym, or athletic club, | ½
|
||
5380
|
Bowling, billiards, pool, etc. | ¯
|
||
5390
|
Skating rinks, roller skates, etc. | |||
5400 | Camps, camping, and related establishments | B
|
||
5500 | Natural and other recreational parks
|
A
|
||
Education, public admin., health care, and other inst.
|
6000 | Education, public admin., health care, and other inst. | ||
6100 | Educational services | |||
6110
|
Nursery and preschool | A
|
||
6120
|
Grade schools | |||
6121
|
Elementary |
|
||
6122
|
Middle | ½
|
||
6123
|
Senior | ½
|
||
6124
|
Continuance | ½
|
||
6125
|
Alternate education services | ½
|
||
6126
|
Adult education services | ½
|
||
6130
|
Colleges and universities | ½
|
||
6140
|
Technical, trade, and other specialty schools | ½
|
||
6141
|
Beauty schools | ½
|
||
6142
|
Business management | ½
|
||
6143
|
Computer training | ¯
|
||
6144
|
Driving education | |||
6145
|
Fine and performing arts education | A
|
||
6146
|
Flight training | U
|
||
6147
|
Sports and recreation education | B
|
||
6200 | Public administration | |||
6210
|
Legislative and executive functions | B
|
||
6220
|
Judicial functions | B
|
||
6221
|
Courts | B
|
||
6222
|
Correctional institutions | A
|
||
6300 | Other government functions | B
|
||
6310
|
Military and national security | |||
6320
|
Space research and technology |
|
||
6400 | Public Safety | ½
|
||
6410
|
Fire and rescue | ¯
|
||
6420
|
Police | |||
6430
|
Emergency response | B
|
||
6500 | Health and human services | |||
6510
|
Ambulatory or outpatient care services | A
|
||
6511
|
Clinics | |||
6512
|
Family planning and outpatient care centers |
|
||
6513
|
Medical and diagnostic laboratories | ½
|
||
6514
|
Blood and organ banks | ¯
|
||
6520
|
Nursing, supervision, and other rehabilitative services | |||
6530
|
Hospital | A
|
||
6560
|
Social assistance, welfare, and charitable services | B
|
||
6561
|
Child and youth services | |||
6562
|
Child day care |
|
||
6563
|
Community food services | ½
|
||
6564
|
Emergency and relief services | ½
|
||
6565
|
Other family services | ¯
|
||
6566
|
Services for elderly and disabled | |||
6567
|
Veterans affairs | B
|
||
6568
|
Vocational rehabilitation | A
|
||
6600 | Religious institutions | A
|
||
6700 | Death care services | B
|
||
6710
|
Funeral homes and services | |||
6720
|
Cremation services and cemeteries |
|
||
6800 | Associations, nonprofit organizations, etc. | ½
|
||
6810
|
Labor and political organizations | ½
|
||
6820
|
Business associations and professional membership organizations | ¯
|
||
6830
|
Civic, social, and fraternal organizations
|
B
|
||
Construction-related businesses
|
7000 | Construction-related businesses | ||
7100 | Building, developing, and general contracting | B
|
||
7110
|
Residential construction | |||
7120
|
Land development and subdivision |
|
||
7130
|
Industrial, commercial and institutional building construction | ½
|
||
7200 | Machinery related | ½
|
||
7210
|
Building equipment and machinery installation contractors | ½
|
||
7220
|
Excavation contractor | ½
|
||
7230
|
Water well drilling contractor | ½
|
||
7240
|
Wrecking and demolition establishment | ½
|
||
7250
|
Structural steel erection contractor | ½
|
||
7300 | Special trade contractor | ½
|
||
7310
|
Carpentry, floor, and tile contractor | ½
|
||
7320
|
Concrete contractor | ½
|
||
7330
|
Electrical contractor | ½
|
||
7340
|
Glass and glazing contractor | ½
|
||
7350
|
Masonry and drywall contractors | ½
|
||
7360
|
Painting and wall covering | ¯
|
||
7370
|
Plumbing, heating, and air-conditioning | |||
7380
|
Roofing, siding, and sheet metal contractors | B
|
||
7400 | Heavy construction | C
|
||
7410
|
Highway and street construction; | |||
7420
|
Bridge and tunnel construction |
|
||
7430
|
Water, sewer, and pipeline construction | ¯
|
||
7440
|
Power lines, communication and transmission lines | |||
7450
|
Industrial and other nonbuilding construction
|
C
|
||
Mining and extraction establishments
|
8000 | Mining and extraction establishments | C
|
|
8100 | Oil and natural gas | |||
8200 | Metals (iron, copper, etc.) |
|
||
8300 | Coal | ¯
|
||
8400 | Nonmetallic mining | |||
8500 | Quarrying and stone cutting establishment
|
C
|
||
Agriculture, forestry, fishing and hunting
|
9000 | Agriculture, forestry, fishing and hunting | ||
9100 | Crop production | C
|
||
9110
|
Grain and oilseed | |||
9111
|
Wheat |
|
||
9112
|
Corn | ½
|
||
9113
|
Rice | ½
|
||
9114
|
Soybean and oilseed | ½
|
||
9115
|
Dry pea and bean | ½
|
||
9120
|
Vegetable farming or growing services | ½
|
||
9130
|
Fruits and trees | ½
|
||
9140
|
Greenhouse, nursery, and floriculture | ½
|
||
9141
|
Food crops grown under cover | ½
|
||
9142
|
Nursery and tree production | ½
|
||
9143
|
Floriculture production | ½
|
||
9150
|
All other crops | ½
|
||
9151
|
Tobacco crop | ½
|
||
9152
|
Cotton crop | ½
|
||
9153
|
Sugarcane crop | ½
|
||
9154
|
Hay | ½
|
||
9155
|
Peanut crop | ½
|
||
9200 | Support functions for agriculture | ½
|
||
9210
|
Farm and farm labor management services | ½
|
||
9220
|
Spraying, dusting, and other related services | ½
|
||
9230
|
Crop harvesting and post harvest crop activities (including drying, siloing, etc.) | ½
½ |
||
9240
|
Cotton ginning, grist milling, etc. | ½
|
||
9300 | Animal production including slaughter | ½
|
||
9310
|
Cattle ranch and crops | ½
|
||
9311
|
Beef cattle ranch establishments | ½
|
||
9312
|
Cattle feedlot establishment | ½
|
||
9320
|
Dairy cattle and milk production | ½
|
||
9330
|
Hog and pig farm | ½
|
||
9340
|
Poultry and egg production and hatcheries | ½
|
||
9350
|
Sheep and goat farming establishments | ½
|
||
9360
|
Fish hatcheries, fisheries, and aquaculture | ½
|
||
9370
|
All other animal production | ½
|
||
9371
|
Apiculture (bees, wax, and related operations) | ½
|
||
9372
|
Horse and equine production | ½
|
||
9373
|
Fur-bearing animal production | ½
|
||
9380
|
Support functions for animal production | ½
|
||
9400 | Forestry and Logging | ½
|
||
9410
|
Logging | ½
|
||
9420
|
Forest nurseries | ½
|
||
9430
|
Support functions for forestry | ½
|
||
9500 | Fishing, hunting and trapping, game preserves | ½
|
||
9510
|
Fishing | ¯
|
||
9520
|
Hunting and trapping, game retreats, game and fishing preserves | C
|
||
9900 | Unclassifiable function | U
|
||
9910
|
Not applicable to this dimension |
|
||
9990
|
To be determined | ¯
|
||
9999
|
To be determined
|
U
|
910.100 | General |
910.102 | Instrumentation |
910.103 | Definitions |
910.104 | Measurement Techniques for 35 Ill. Adm. Code 900 |
910.105 | Measurement Techniques for 35 Ill. Adm. Code 901 |
910.106 | Protocols for Determination of Sound Levels |
910.107 | Measurement Techniques for Highly-Impulsive Sound Under 35 Ill. Adm. Code 104 |
910.APPENDIX A | |
Tables of Long-Term Background Ambient Noise |
910. TABLE A | Daytime long-term background ambient Leq levels in decibels by land use categories and 1/3 octave-band level |
910. TABLE B | Nighttime long-term background ambient Leq levels in decibels by land use categories and 1/3- octave-band level |
910. TABLE C | Daytime long-term background ambient Leq levels in decibels by land use categories and octave-band level |
910. TABLE D | Nighttime long-term background ambient Leq levels in decibels by land use categories and octave-band level |
Section 910.100 | General |
1) | An integrating sound level meter used alone or used in conjunction with an octave-band or 1/3 octave-band filter set or a real-time sound analyzer (octave-band or 1/3 octave-band) must conform with the following standards incorporated by reference at 35 Ill. Adm. Code 900.106: |
A) | ANSI S1.4 – 1983 (R2001) “American National Standard Specification for Sound Level Meters”, and ANSI S1.4 A-1985 “Amendment to ANSI S1.4-1983.” |
B) | ANSI S1.11 - 1986 (R1998) “American National Standard Specifications for Octave-Band and Fractional-Octave-Band Analog and Digital Filters.” |
C) | ANSI S1.6 – 1984 (R2001) “American National Standard Preferred Frequencies, Frequency Levels, and Band Numbers for Acoustical Measurements.” |
D) | ANSI S1.8 - 1989 “American National Standard Reference Quantities for Acoustical Levels.” |
E) | International Electrotechnical Commission, IEC 804-2000 Integrating/Averaging Sound level meters. | ||
2) | A magnetic tape recorder, graphic level recorder or other indicating device used must meet the requirements of the Society of Automotive Engineers (SAE) Recommended Practice J184 “Qualifying a Sound Data Acquisition System,” November 1998, incorporated by reference at 35 Ill. Adm. Code 900.106 | ||
3) | The laboratory calibration of instrumentation used for acoustic measurement must be traceable to the National Bureau of Standards, and must be performed no less often than once every 12 months. | ||
4) | For outdoor measurement, a windscreen must be attached to the microphone. | ||
1) | An anemometer and compass or other devices must be used to measure wind speed and direction in accordance with the manufacturer's recommended procedures. |
2) | A thermometer, designed to measure ambient temperature, must be used in accordance with the manufacturer's recommended procedures. |
3) | A hygrometer must be used in accordance with the manufacturer's recommended procedures to measure the relative humidity. |
4) | A barometer must be used in accordance with the manufacturer's recommended procedures to measure the barometric pressure. |
Section 910.103 | Definitions |
The definitions contained in 35 Ill. Adm. Code 900.101 apply to this Part. | |
Section 910.104 | Measurement Techniques for 35 Ill. Adm. Code 900 |
Section 910.105 | Measurement Techniques for 35 Ill. Adm. Code 901 |
a) | Site Selection |
1) | Measurements may be taken at one or more microphone positions within the appropriate receiving land. Measurement instruments must be set up outdoors within the boundaries of the receiving land for the purpose of determining whether a noise source is in compliance with 35 Ill. Adm. Code 901. |
2) | Measurement instruments must be set up not less than 25 feet (7.6 meters (m)) from the property-line-noise-source. The 25-foot (7.6 m) setback requirement is from the noise source and not the property line unless the noise source is contiguous to the property line. |
3) | Other measurement locations may be used for investigatory purposes such as, but not limited to, the following: |
A) | Determining the extent of noise pollution caused by the source of sound; |
B) | Determining the ambient; and |
C) | Analyzing those acoustical parameters that describe the sound source. |
4) | For measurements of sound sources with no audible discrete tones, microphones should not be set up less than 25 feet (7.6 m) from any reflective surface that may affect data. If measurements must be taken within 25 feet (7.6 m), the effect, if any, of the reflective surface on the measured data must be determined. |
5) | For measurements of sound sources with audible discrete tones, microphones must not be set up less than 50 feet (15.2 m) from any reflective surface that may affect data. If measurements must be taken within 50 feet (15.2 m), the effect, if any, of the reflective surface on the measured data must be determined. |
6) | Objects with small dimensions (trees, posts, bushes, etc.) must not be within 5 feet (1.5 m) of the microphone position. If measurements must be taken within 5 feet (1.5 m) of such objects, the effect, if any, on the measured data must be determined. |
b) | Instrumentation Set Up |
1) | A tripod must be set at the chosen site. The tripod must be extended to a height between 3 feet 8 inches (1.12 m) and 4 feet 10 inches (1.47 m) above ground. |
2) | A microphone must be attached to the appropriate end of a 5-foot (1.5 m) or longer cable and must be affixed to the top of the tripod. The other end of the cable must be connected to the measuring instrument. |
3) | The angle of incidence of the microphone must be adjusted to yield the flattest frequency response in accordance with the manufacturer’s specifications. |
4) | The measuring instrument must be separated from the microphone so as to minimize any influence on the measurements. The cable movement must be minimized during the measurement period. |
c) | Measurement Site Operation and Instrument Calibration |
1) | Before taking sound pressure level measurements, measure and record (near the measurement site): |
A) | Wind speed and direction; |
B) | Ambient temperature; |
C) | Relative humidity; and |
D) | Barometric pressure. |
2) | Turn the measuring instrument on and allow the instrument to stabilize. Monitor and record the battery condition of the calibrator and all measuring instruments. |
3) | Turn the calibrator on at its appropriate frequency. Allow the calibrator to stabilize and calibrate the measuring system according to the manufacturer's specifications. After the measuring system has been calibrated, remove the calibrator and attach a windscreen to the microphone. |
4) | Adjust the microphone to the angle of incidence that will yield the frequency response in accordance with the manufacturer's specifications. |
5) | Measure the sound pressure level data within the limitations of subsection (d) and according to the manufacturer's recommended procedures. Other sound pressure levels may be used for investigatory purposes such as, but not limited to, the following: |
A) | Determining the extent of noise pollution caused by the source of sound; |
B) | Determining the ambient; and |
C) | Analyzing those acoustical parameters that describe the sound source. |
6) | While sound measurements are being taken, the operator must be separated from the microphone so as to minimize any influence on the measurements. |
7) | While measurements are being taken, visual and aural surveillance of extraneous sound sources and varying wind conditions must be made to insure that the conditions of measurement are accurately known. Record any variations in these parameters that may affect data. The number and basis for affected data block must be recorded. When using a tape recorder, voice commentary concerning conditions will be recorded on the cue track. |
8) | To minimize wind effects on the microphone, sound measurements must not be taken when the wind velocity is greater than 12 miles per hour (5.4 m/second) at the microphone position. |
9) | For the purposes of data correction, the ambient sound at the measurement site must be determined by means of measurement or analysis. |
10) | After taking sound pressure level measurements, remove the windscreen and attach the calibrator to the microphone. Turn the calibrator on at its appropriate frequency. After allowing the calibrator to stabilize, monitor and record the measuring system response. When the measuring system response varies by more than + 0.5 dB from the most recent field calibration, the sound pressure level measurements obtained since such most recent field calibration cannot be used for enforcement purposes. |
11) | Before removing the calibrator from the microphone, turn the calibrator off. If the ambient sound has not been determined by means of measurement, determine the noise floor of the measuring system. If the noise floor is within 10 dB of the measured sound pressure level data, such noise floor measurements must be recorded. |
12) | At the end of the sound survey, monitor and record the battery condition of the calibrator and all measuring instruments. Near the measurement site, measure and record: |
A) | Windspeed and direction; |
B) | Ambient temperature; |
C) | Relative humidity; and |
D) | Barometric pressure. |
13) | Record the physical and topographical description of the ground surface within the vicinity of the measurement site, survey site location, a description of the sound source, a diagram of the area, the location of reflective surfaces near the microphone, and the approximate location of the noise source relative to the microphone position. |
14) | A magnetic tape recorder may be used to preserve the raw data. Calibration signals must be recorded at the beginning and end of each tape as well as at intermediate times such as when relocating to a new measurement site. Voice commentary concerning local conditions and affected data blocks must be recorded on the cue track. The original tape recording must be preserved for subsequent evaluation. Laboratory analyses may be performed on magnetic tape recorded field data. A description of the laboratory instrumentation and procedures must be recorded. Analyses used in the laboratory must be correlated to field measurement techniques. |
d) | Limiting Procedures for Specific Types of Data Acquisition |
1) | For measurements of non-impulsive sound with audible discrete tones, 1/3 octave-band sound pressure levels must be obtained in determining whether a noise source is in compliance with 35 Ill. Adm. Code 901.106. |
2) | For measurements of non-impulsive sound with no audible discrete tones, octave-band sound pressure levels must be obtained in determining whether a noise source is in compliance with 35 Ill. Adm. Code 901.102 and 901.103. |
e) | Correction Factors |
a) | The raw data collection procedures for the determination of equivalent continuous sound pressure level (Leq) are described in this Section using as an example the determination of a 1-hour Leq corrected for ambient. The following procedures must be used: |
A) | The 1-hour interval is divided into many small blocks of time so that corruption of the data from short-term background transient sound and loss of data can be limited to the corrupted or bad blocks. The block duration in seconds must remain fixed for any measurement hour. The duration must be neither less than 10 seconds nor greater than 100 seconds. For example, if the block duration is chosen to be 60 seconds (1 minute), then the data collection proceeds for 60, 1-minute periods of measurement. |
B) | The collected data for each block represents a block duration Leq (or sound exposure level (SEL)) in octave-bands (or 1/3 octave-bands if prominent discrete tones may be present). |
C) | Data for any block corrupted by one or more short-term background transient sounds must be deleted. |
D) | After deleting corrupted data blocks, there will be a fixed number of “good” data blocks remaining. This number is designated as NPLNS, where PLNS stands for Property-Line-Noise-Source. These remaining “good” blocks must be numbered consecutively. The subscript i is used to denote the numbering of the blocks in time order after corrupted data blocks have been deleted. |
E) | The data for the NPLNS remaining blocks are time averaged on an energy basis by octave (or 1/3 octave-band) using Equation 1 below. In this equation, two subscripts are used, i to designate time and j to designate the specific frequency, either an octave-band or 1/3 octave-band. The raw, 1-hour Leq in the jth frequency band is given by: | ||
F) | In terms of SEL, the raw SEL in the jth frequency band is given by: |
G) | The raw, 1-hour Leq in the jth frequency band is given in terms of the corresponding SELj by: |
A) | The measuring instrument must be adjusted to continuously measure sound pressure and accumulate Leq for each block of time. For convenience, the hour may be split into several smaller blocks such as 10, 6-minute blocks or 4, 15-minute blocks, etc. |
B) | A switch on the measuring instrument must be available to inhibit data collection whenever a short-term background transient sound occurs. This switch shall be used to prevent short-term background ambient sounds from corrupting the data. |
C) | Data collection must proceed for one hour. The energy average of the several measured Leqij each weighted by the number of seconds actually accumulated during the ith block results in the raw, 1-hour Leq in each frequency band given by: |
3) | Minimum data collection requirements: |
A) | Initial Measurement Duration. The property-line-noise-source measurements must proceed initially for one hour. Because of correction for short-term background transient sounds, actual reported data collection time T, in seconds, may be less than 3600 seconds (one hour). |
i) | If small blocks of data are used for data collection, then the total measurement duration in seconds, TPLNS, is given by NPLNS T, where T is the length of each block in seconds and NPLNS is the number of non-discarded blocks. If data inhibition is used for data collection, then TPLNS is the number of non-inhibited seconds during the measurement hour. In either case, TPLNS must be no less than 900 seconds. |
ii) | If very few blocks were used for data collection, then the duration of each block, T, may be too long and should be reduced. |
iii) | For either data collection method, sounds considered to be short-term transient may actually be part of the long-term background ambient and should be so redefined. |
B) | Extended Measurement Duration. If TPLNS is less than 900 seconds during the first hour of measurements, the raw data collection procedures must be appropriately modified and new measurements must proceed for an additional hour. If TPLNS after combining the first and the second hour of measurements is also less than 900 seconds, then the raw data collection must continue using the data inhibition method or method employed during the second hour until TPLNS is greater than or equal to 900 seconds. |
4) | Correction for Long-Term Background Ambient Sound: |
A) | The raw 1-hour Leq must be corrected for long-term background ambient sound. The subsection below describes methods to obtain the long-term background ambient sound level in the jth frequency band. The correction is dependent on the difference (in decibels) between the raw, 1-hour, jth band property-line-noise-source: Leqj and corresponding jth band long-term background ambient sound level. The correction to be applied is as follows: |
i) | If the difference between the raw 1-hour Leq and the long-term background ambient sound is larger than 10 decibels, then the correction must be set to 0. |
ii) | If the difference between the raw 1-hour Leq and the long-term background ambient sound difference is less than 3 decibels, then the jth frequency-band level, Leqj, must be set equal to 0. |
iii) | If the difference between the raw 1-hour Leq and the long-term background ambient sound is between 3 and 10 decibels, then the correction given in Table 1 below must be subtracted from the raw, 1-hour property-line-noise-source Leqj |
Difference
|
Correction
|
|
(dB)
|
(dB)
|
|
3
|
3
|
|
4
|
2.3
|
|
5
|
1.7
|
|
6
|
1.3
|
|
7
|
1.0
|
|
8
|
0.7
|
|
9
|
0.6
|
|
10
|
0.5
|
B) | The long-term background ambient corrected level must be the property-line-noise-source Leqj reported for the jth frequency band. |
1) | The background ambient must be measured for the purposes of this Section during a 10-minute interval. |
2) | Long-term background ambient measurement procedures are similar to procedures to measure the property-line-noise-source itself. Eliminating short-term background ambient transient sounds from the measurement of average long-term background ambient sound proceeds in a manner similar to the measurement of the property-line-noise-source emissions themselves. The two methods for measurement are: to divide the 10-minute measurement into short blocks of data, or inhibit data collection when short-term background transient sounds occur. The same method must be used for gathering both the property-line-noise-source data and the corresponding long-term background ambient data. The measurement procedures for each method are given in subsections (b)(3), (b)(4) and (b)(5) of this Section: |
3) | Using Small Blocks of Data |
A) | The 10-minute measurement of long-term background ambient must be divided into short measurement blocks. The duration of these blocks must remain constant during the entire measurement, both when measuring the long-term background ambient and when measuring the property-line-noise-source. The duration of this measurement block in seconds, T, must divide exactly (without remainder) into 600 and must be neither greater than 100 seconds nor less than 10 seconds. |
B) | All data for any measurement block corrupted by one or more short-term ambient transient sounds must be discarded. The number of remaining, non-discarded measurement blocks is designated NBA, where BA stands for background ambient. |
C) | The Leq for each octave-(or 1/3 octave-) band are time-averaged on an energy basis over the NBA remaining measurement blocks to obtain average long-term background ambient Leq per band. Equation 1 (see subsection (a) (1) (E) of this Section) is used for this calculation with NBA replacing NPLNS as the number of elemental blocks to be summed. The total duration of the measurement in seconds, TBA, is given by NBA multiplied by T. |
A) | The measuring instrument must be adjusted according to manufacturer’s instructions to continuously measure sound pressure and accumulate (i.e. record) Leq. A switch must be available to inhibit data collection whenever a short-term background transient sound occurs, (and on some instruments, a button may be available to delete the most recent, previous data). |
B) | The switches or buttons must be used to prevent short-term background ambient sounds from corrupting the data. |
C) | Data collection must proceed for 10 minutes. The result is the 10-minute, long-term background ambient Leq in each band. |
D) | TBA is the number of non-inhibited measurement seconds during the 10-minute measurement period. |
5) | The minimum duration, for either method, TBA must be no less than 150 seconds. If TBA is less than 150 seconds, then the measurement of the long-term background ambient must continue beyond the original 10 minutes and until TBA for the total long-term background ambient measurement is greater than or equal to 150 seconds. |
6) | Measurement Alternatives. The long-term background ambient noise should ideally be measured at the potential violation site just before measurement of the property-line-noise-source emissions. However, turning off the property-line-noise-source may not always be possible. The following are a hierarchical order of five procedures for obtaining the long-term background ambient noise. The first four procedures involve direct measurement; the fifth procedure provides for use of tables of values obtained from extensive measurements. These are not equivalent procedures but are ordered from what is considered to be the most accurate to what is considered to be the least accurate procedure. |
A) | Direct Measurement Procedure –1: With the property-line-noise-source (PLNS) turned off, measure the long-term background ambient noise within the hour before or within the hour after measurement of the PLNS emissions at the location where the PLNS measurements are being taken and with the measurement equipment used for the PLNS measurements. |
B) | Direct Measurement Procedure-2: With the PLNS turned off, measure the long-term background ambient during a similar time period in terms of background ambient sound level, within one to 24 hours before, or within one to 24 hours after measurement of the PLNS emissions at the location where the PLNS measurements are being taken and with the measurement equipment used for the PLNS. |
C) | Direct Measurement Procedure- 3: With the PLNS turned off, measure the long-term background ambient during some other acoustically similar period within one to 30 days before, or within one to 30 days after measurement of the PLNS emissions. This alternate long-term background ambient measurement time might be a Saturday night or anytime during a Sunday or holiday. The measurements would be made at the location where the PLNS measurements are being taken and with the measurement equipment (or like equipment) used for the PLNS measurement. |
D) | Direct Measurement Procedure-4: With the PLNS turned off, measure the long-term background ambient noise during some other acoustically similar period within 30 to 90 days before, or within 30 to 90 days after measurement of the PLNS emissions. These measurements would be made at the location where the PLNS measurements are being taken and with the measurement equipment (or like equipment) used for the property-line-noise-source measurements. |
E) | Tables of Long-Term Background Ambient Noise. Where none of the alternatives can be used, use the applicable long-term background ambient data taken from Tables A through D in Appendix A of this Part. These tables are organized by predominant land use and time of day (daytime or nighttime). There are separate tables for octave- and 1/3- octave-bands. The background environments presented in the table are based on extensive measurements conducted in the Chicago area and are divided into the five categories given below in accordance with G.L. Bonvallet, “Levels and Spectra of Traffic, Industrial, and Residential Area Noise,” Journal of the Acoustical Society of America, 23 (4), pp 435-439, July 1951; and Dwight E. Bishop and Paul D. Schomer, Handbook of Acoustical Measurements and Noise Control, Chapter 50, Community Noise Measurements, 3rd Edition, Cyril M Harris, Editor, McGraw-Hill Book Co., New York (1991). |
i) | Category 1: Noisy Commercial and Industrial Areas. Very heavy traffic conditions, such as in busy downtown commercial areas, at intersections of mass transportation and other vehicles, including the Chicago Transit Authority trains, heavy motor trucks and other heavy traffic, and street corners where motor buses and heavy trucks accelerate. |
ii) | Category 2: Moderate Commercial and Industrial Areas, and Noisy Residential Areas. Heavy traffic areas with conditions similar to subsection (b)(6)(E)(i) of this Section but with somewhat less traffic, routes of relatively heavy or fast automobile traffic but where heavy truck traffic is not extremely dense, and motor bus routes. |
iii) | Category 3: Quiet Commercial and Industrial Areas, and Moderate Residential Areas. Light traffic conditions where no mass transportation vehicles and relatively few automobiles and trucks pass, and where these vehicles generally travel at low speeds. Residential areas and commercial streets and intersections with little traffic comprise this category. |
iv) | Category 4: Quiet Residential Areas. These areas are similar to Category 3 in subsection (b)(6)(E)(iii) of this Section but, for this group, the background is either distant traffic or is unidentifiable. |
v) | Category 5: Very Quiet, Sparse Suburban or Rural Areas. These areas are similar to Category 4 subsection (b)(6)(E)(iv) of this Section but are usually in unincorporated areas and, for this group, there are few if any near neighbors. |
Section 910.107 | Measurement Techniques for Highly-Impulsive Sound Under 35 Ill. Adm. Code 901.104. |
a) | Measurement of highly-impulsive sound under 35 Ill. Adm. Code 901.104 can be made in two distinct and equally valid ways, namely the general method and the controlled test method. |
b) | General Method: The general method is to measure the 1-hour, A-weighted Leq (not the octave- or 1/3 octave-band levels) using essentially one of the two procedures described in Sections 910.105 and 910.106. |
A) | The hour must be divided into small blocks and the A-weighted Leq must be measured for each of these small blocks of time. Leq must be measured for the entire hour but data collection must be inhibited whenever a short-term background transient sound occurs. |
B) | The duration of each block must be held constant during the hour. This duration in seconds must divide exactly into 900 and must be neither greater than 100 seconds nor less than 10 seconds. |
C) | The data for any block corrupted by one or more short-term background ambient sounds must be discarded. |
B) | Data collection must be inhibited whenever a short-term background transient sound occurs. |
3) | Correction for the long-term background ambient must be accomplished using all of the other procedures and requirements enumerated in Sections 910.105 and 910.106. These requirements must be complied with to determine an A-weighted, 1-hour, background-ambient-corrected Leq for the highly impulsive property-line-noise-source under study. |
A) | The sound exposure per impulse from each separate individual impulsive source is measured. |
B) | The total sound exposure per hour from each source is the sound exposure per event multiplied by the number of events per hour. |
C) | The grand total sound exposure (SE) per hour is the sum of the sound exposures per hour from each of the separate individual sources. |
D) | The reported SEL is obtained from the grand total sound exposure (SE) per hour using the following: |
E) | The equivalent level, Leq corresponding to a SEL measured or predicted for one hour (3600 seconds) is given by: |
A) | The sound exposure per event from each, separate, individual source must be determined by measuring the total A-weighted sound exposure for about 10 repetitions of this source. This set of about 10 measurements may be performed continuously over a short period of time, or this set of measurements may be performed over a discontinuous set of measurement periods. In either case, the total measurement duration must be less than 100 seconds. |
B) | These separate, individual property-line-noise- source controlled measurements must be free of any short-term ambient sounds. If any short-term background transient sounds occur during these measurements, then the measurement must be repeated until measurement data, free of any corrupting short-term background ambient sounds, are obtained. |
C) | The total measured A-weighted sound exposure for this group of about 10 repetitions must be corrected for long-term background ambient by subtracting the A-weighted long-term background ambient sound exposure. The sound exposure value subtracted must be the long-term A-weighted background ambient sound exposure per second multiplied by the number of seconds used to measure the several source repetitions. |
D) | The reported Source: A-weighted sound exposure per event must be the total corrected sound exposure divided by the number of source repetitions measured. |
E) | The background ambient must be measured for a short time, at least 30 seconds as near in time to the source measurements as possible, but within ½ hour. The total A-weighted long-term background ambient sound exposure per second is the total measured long-term background ambient sound exposure divided by the number of seconds of background ambient measurement. |
F) | There must be no short-term background ambient sounds present during the measurement of the long-term background ambient. If any short-term background transient sounds occur during these measurements, then the measurements must be repeated until long-term background ambient measurement data free of any corrupting short-term background ambient sound are obtained. |
Background Category
|
Octave-Band Center Frequency (Hz)
|
1
|
2
|
3
|
4
|
5
|
20
|
63
|
56
|
48
|
42
|
36
|
25
|
64
|
57
|
49
|
43
|
37
|
31
|
65
|
58
|
50
|
44
|
38
|
40
|
65
|
58
|
51
|
44
|
38
|
50
|
66
|
59
|
51
|
45
|
39
|
63
|
66
|
59
|
52
|
46
|
40
|
80
|
67
|
60
|
52
|
46
|
40
|
100
|
68
|
60
|
53
|
47
|
41
|
125
|
67
|
59
|
52
|
46
|
40
|
160
|
66
|
59
|
52
|
46
|
40
|
200
|
66
|
58
|
51
|
45
|
39
|
250
|
65
|
58
|
50
|
44
|
38
|
315
|
64
|
57
|
49
|
43
|
37
|
400
|
63
|
55
|
48
|
42
|
36
|
500
|
62
|
54
|
46
|
40
|
34
|
630
|
61
|
53
|
44
|
38
|
32
|
800
|
60
|
51
|
42
|
36
|
30
|
1000
|
58
|
49
|
40
|
34
|
28
|
1250
|
56
|
47
|
38
|
32
|
26
|
1600
|
54
|
45
|
36
|
30
|
24
|
2000
|
52
|
43
|
33
|
28
|
21
|
2500
|
50
|
41
|
30
|
25
|
19
|
3150
|
49
|
39
|
28
|
23
|
17
|
4000
|
48
|
37
|
25
|
20
|
15
|
5000
|
46
|
35
|
23
|
18
|
13
|
6300
|
44
|
33
|
21
|
16
|
10
|
8000
|
43
|
31
|
19
|
14
|
8
|
10,000
|
41
|
29
|
17
|
12
|
6
|
12,500
|
39
|
27
|
15
|
10
|
4
|
Background Category
|
Octave-Band Center Frequency (Hz)
|
1
|
2
|
3
|
4
|
5
|
20
|
53
|
48
|
43
|
37
|
31
|
25
|
54
|
49
|
44
|
38
|
32
|
31
|
55
|
50
|
45
|
39
|
33
|
40
|
55
|
50
|
46
|
39
|
33
|
50
|
56
|
51
|
46
|
40
|
34
|
63
|
56
|
51
|
47
|
41
|
35
|
80
|
57
|
52
|
47
|
41
|
35
|
100
|
58
|
52
|
48
|
42
|
36
|
125
|
57
|
51
|
47
|
41
|
35
|
160
|
56
|
51
|
47
|
41
|
35
|
200
|
56
|
50
|
46
|
40
|
34
|
250
|
55
|
50
|
45
|
39
|
33
|
315
|
54
|
49
|
44
|
38
|
32
|
400
|
53
|
47
|
43
|
37
|
31
|
500
|
52
|
46
|
41
|
35
|
29
|
630
|
51
|
45
|
39
|
33
|
27
|
800
|
50
|
43
|
37
|
31
|
25
|
1000
|
48
|
41
|
35
|
29
|
23
|
1250
|
46
|
39
|
33
|
27
|
21
|
1600
|
44
|
37
|
31
|
25
|
19
|
2000
|
42
|
35
|
28
|
23
|
16
|
2500
|
40
|
33
|
25
|
20
|
14
|
3150
|
39
|
31
|
23
|
18
|
12
|
4000
|
38
|
29
|
20
|
15
|
10
|
5000
|
36
|
27
|
18
|
13
|
8
|
6300
|
34
|
25
|
16
|
11
|
5
|
8000
|
33
|
23
|
14
|
9
|
3
|
10,000
|
31
|
21
|
12
|
7
|
1
|
12,500
|
29
|
19
|
10
|
2
|
|
Background Category
|
Octave-Band Center Frequency (Hz)
|
1
|
2
|
3
|
4
|
5
|
31
|
70
|
63
|
55
|
49
|
43
|
63
|
71
|
64
|
57
|
51
|
45
|
125
|
72
|
64
|
57
|
51
|
45
|
250
|
70
|
63
|
55
|
49
|
43
|
500
|
67
|
59
|
51
|
45
|
39
|
1000
|
63
|
54
|
45
|
39
|
33
|
2000
|
57
|
48
|
38
|
33
|
26
|
4000
|
53
|
42
|
30
|
25
|
20
|
8000
|
48
|
36
|
24
|
19
|
13
|
Background Category
|
Octave-Band Center Frequency (Hz)
|
1
|
2
|
3
|
4
|
5
|
31
|
60
|
55
|
50
|
44
|
38
|
63
|
61
|
56
|
52
|
46
|
40
|
125
|
62
|
56
|
52
|
46
|
40
|
250
|
60
|
55
|
50
|
44
|
38
|
500
|
57
|
51
|
46
|
40
|
34
|
1000
|
53
|
46
|
40
|
34
|
28
|
2000
|
47
|
40
|
33
|
28
|
21
|
4000
|
43
|
34
|
25
|
20
|
15
|
8000
|
38
|
28
|
19
|
14
|
8
|