App A - Acoustic Report - Minor Change - 12.08.2025.pdf

Sunshine Beach Surf Club                                                                                                           Reference: #1721d1-C
Belmore Terrace, Sunshine Beach QLD 4567                                                                                         Date: 12 November 2024
Entertainment Noise Assessment
            Table 1: Background LA90 noise level record and calculation sheet for amplified music and patron noise assessment - pre-6pm
 PRE        RAP.2 - 7 Webb Rd - SLPA7
 6PM                    Measurement Details                          Wind           Noise                  Octave band centre frequencies
                                                                                                                                                             Overall
           Location Number         Start Time Duration         Speed      Direction Descr-      63       125       250       500       1000        2000
Row 1-1       BG1          1         21:35:46     10 mins     < 2m/s       CALM      L90     55 dBZ    52 dBZ     51 dBZ    51 dBZ    48 dBZ      45 dBZ     59 dBZ
Row 1-2     Minus insects/frogs (if applicable)                                               0 dBZ     0 dBZ     0 dBZ     0 dBZ     0 dBZ        0 dBZ
Row 1-3     Plus non-standard windscreen attenuation (if applicable)                          0 dBZ     0 dBZ     0 dBZ     0 dBZ     0 dBZ        0 dBZ
Row 1-4     'A' frequency weighting adjustment figures                                         -26       -16        -9        -3         0           1
Row 1-6     Calculated LA90                                                          L90     29 dBA 36 dBA 42 dBA 48 dBA 48 dBA                   46 dBA     53 dBA
Row 1-7     Overall intrusive noise limit (LA90 + 10dBA)                             L10                                                                     63 dBA

            Table 2: Intrusive noise measurement data, normalisation & calculation of maximum noise limits to prevent unreasonable noise - pre-6pm
 PRE        Scenario 3 - RAP.2 - 7 Webb Rd - SLPA7
 6PM                    Measurement Details                           Wind            Noise                      Octave band centre frequencies
                                                                                                                                                             Overall
           Location Number          Start Time Duration          Speed      Direction Descr-        63         125        250       500      1000   2000
Row 2-1       L3          32       10:02:14 AM 3 mins            < 2m/s         S       L10      59 dBZ      59 dBZ     57 dBZ    56 dBZ    53 dBZ 43 dBZ    64 dBZ
Row 2-2     Minus insects/frogs (if applicable)                                                   0 dBZ       0 dBZ      0 dBZ     0 dBZ     0 dBZ 0 dBZ
Row 2-3     Plus non-standard windscreen attenuation (if applicable)                              0 dBZ       0 dBZ      0 dBZ     0 dBZ     0 dBZ 0 dBZ
Row 2-4     'A' frequency weighting adjustment figures                                             -26         -16         -9        -3        0      1
Row 2-5     Calculated Intrusive noise level                                            L10     33 dBA 43 dBA 48 dBA 53 dBA 53 dBA 44 dBA                    57 dBA
Row 2-6       L3          32       10:02:14 AM 3 mins            < 2m/s         S       L10      59 dBZ      59 dBZ     57 dBZ    56 dBZ    53 dBZ 43 dBZ    64 dBZ
Row 2-7     Minus insects/frogs (if applicable)                                                   0 dBZ       0 dBZ      0 dBZ     0 dBZ     0 dBZ 0 dBZ
Row 2-8     Plus non-standard windscreen attenuation (if applicable)                              0 dBZ       0 dBZ      0 dBZ     0 dBZ     0 dBZ 0 dBZ
Row 2-9     'A' frequency weighting adjustment figures                                             -26         -16         -9        -3        0      1
Row 2-10    Calculated Intrusive noise level                                            L10     33 dBA 43 dBA 48 dBA 53 dBA 53 dBA 44 dBA                    57 dBA
Row 2-11      L3          32       10:02:14 AM 3 mins            < 2m/s         S       L10      59 dBZ      59 dBZ     57 dBZ    56 dBZ    53 dBZ 43 dBZ    64 dBZ
Row 2-12    Minus insects/frogs (if applicable)                                                   0 dBZ       0 dBZ      0 dBZ     0 dBZ     0 dBZ 0 dBZ
Row 2-13    Plus non-standard windscreen attenuation (if applicable)                              0 dBZ       0 dBZ      0 dBZ     0 dBZ     0 dBZ 0 dBZ
Row 2-14    'A' frequency weighting adjustment figures                                             -26         -16         -9        -3        0      1
Row 2-15    Calculated Intrusive noise level                                            L10     33 dBA 43 dBA 48 dBA 53 dBA 53 dBA 44 dBA                    57 dBA
Row 2-11                                                                                L10                                                                   0 dBZ
Row 2-12    Minus insects/frogs (if applicable)                                                   0 dBZ       0 dBZ      0 dBZ     0 dBZ     0 dBZ 0 dBZ
Row 2-13    Plus non-standard windscreen attenuation (if applicable)                              0 dBZ       0 dBZ      0 dBZ     0 dBZ     0 dBZ 0 dBZ
Row 2-14    'A' frequency weighting adjustment figures                                             -26         -16         -9        -3        0      1
Row 2-15    Calculated Intrusive noise level                                            L10    -26 dBA -16 dBA -9 dBA             -3 dBA    0 dBA  1 dBA     5 dBA
Row 2-16    SLPA7         24        9:44:47 AM     3 mins        < 2m/s         S       L10    105 dBZ 107 dBZ 101 dBZ 97 dBZ               98 dBZ 94 dBZ   111 dBZ
                             A-Weighted SLPA Source Measurement                         L10     79 dBA 91 dBA 92 dBA 94 dBA 98 dBA 95 dBA                   102 dBA
Row 2-17    Normalisation Moderator                                                            105 dBZ 109 dBZ 100 dBZ 99 dBZ               96 dBZ 95 dBZ   102 dBA
Row 2-18    Normalised Adj. (reference - measured levels) (Row 2-17 minus Row 2-16)               0 dBZ       2 dBZ     -1 dBZ     3 dBZ    -2 dBZ 1 dBZ
Row 2-19    Normalised intrusive noise levels, L10, (Row 2-18 plus Row 2-1, 2-2 or 2-3, L10
                                                                                        whichever59isdBZ
                                                                                                      applicable)
                                                                                                             61 dBZ 55 dBZ 58 dBZ 51 dBZ 44 dBZ              65 dBZ
Row 2-20    'A' frequency weighting adjustment figures                                             -26         -16         -9        -3        0      1
Row 2-21    'A' Weighted normalised intrusive noise level, L10                          L10     33 dBA 45 dBA 46 dBA 55 dBA 51 dBA 45 dBA                    57 dBA
Row 2-22    Noise character                                                                                                                                     8
Row 2-23    Adjusted intrusive noise level due to noise character                                                                                            57 dBA
Row 2-24    Noise limit at affected premises (Row 1-7)                                                                                                       63 dBA
Row 2-25    Difference between intrusive & noise limit at affected premises                                                                                  -5 dBA
Row 2-26    Maximum noise level at Reference Point Location (RPL)                                                                                            62 dBA
Row 2-27    Maximum noise level at Close External Monitoring Location (CEML)                                                                                 62 dBA
Row 2-27    Maximum noise level at Close External Monitoring Location (CEML)
Row 2-28    Maximum noise level at Specific Licensed Premises Area (Source)                                                                                 107 dBA




Live It Acoustics | Controlled Document v1.0                                                                                                                Page 66