8.1
Thirty days of
acoustic monitoring surveys were conducted between 15 January and 22 February 2013
for the baseline period. During this period, 1,885 km of survey effort were
conducted to search for dolphins in the western and northwestern waters of Lantau. A total of 196 groups, numbering 694
dolphins, were sighted during these surveys, and 238 sound samples were taken
from some of these dolphin groups.
8.2
The data
obtained during the initial phase provide a pre-construction baseline for
measuring the potential consequences of construction activities on dolphin behaviour. The dolphin acoustic activities measured using
both acoustic survey and passive acoustic monitoring methods provide
quantitative metrics against which to measure any changes in the behaviour or occurrence of dolphins near the bridge
construction area once construction has begun.
8.3
Major
findings from the analysis of the above data are summarized as follows:
· The
calibrated hydrophone data showed a general increase in whistles and clicks by
group size, and most of these sounds occurred during socializing.
· The
EAR(ecological acoustic recorders) data showed a lull in recorded dolphin
sounds in mid-month and a tendency for some changes in diel
sound (or dolphin occurrence) structure.
· Acoustic
activity levels increased with group size and were highest during socializing
periods. Larger groups have more animals that can contribute signals to
recordings and it is common for dolphins to be more vocally active during
periods of socializing.
· The
EAR data indicate that dolphin acoustic activity is greater at site Fan Lau than
at bridge alignment area. In addition, the average number of daily encounters
and the duration of encounters were greater at site Fan Lau than at bridge
alignment area. More dolphin activity was recorded at Fan Lau despite the
higher ambient noise levels occurring there compared to bridge alignment area.
· Bridge
alignment exhibited a diel pattern of activity while
the control site (Fan Lau) did not, suggesting a differential pattern of
habitat use.
·
The numerical summary of the monitoring results
is presented in Tables 8.1.
Table 8.1
Values of the two response variables of dolphin acoustic behaviour collected by calibrated hydrophone (average
clicks and whistles per minutes) by size of group, behavioural
state and time of day
|
Average clicks |
Average whistles |
|
per minute ( ± s.d.) |
per minute ( ± s.d.) |
|
|
|
Group Size |
|
|
1 dolphins |
62.19 ± 77.73 (n=20) |
0.21 ± 1.49 (n=20) |
2-6 dolphins |
54.03 ± 179.32 (n=125) |
0.56 ± 1.70 (n=12) |
6-9 dolphins |
118.00 ± 310.31 (n=37) |
1.58 ± 4.63 (n=37) |
10+ dolphins |
289.33 ± 140.58 (n=35) |
2.74 ± 1.99 (n=35) |
|
|
|
Behavioural
State |
|
|
Feeding |
30.95 ± 69.90 (n=28) |
0.62 ± 1.33 (n=28) |
Milling |
71.29 ± 205.44 (n=138) |
0.66 ± 1.85 (n=138) |
Socializing |
287.48 ± 326.22 (n=25) |
3.78 ± 4.14 (n=25) |
Traveling |
13.16 ± 208.94 (n=11) |
0.25 ± 1.48 (n=11) |
Resting |
0.10 ± 70.35 (n=5) |
0.13 ± 1.43 (n=5) |
|
|
|
Time of day |
|
|
09:00-10:59 |
38.14 ± 69.90 (n=28) |
0.70 ± 1.33 (n=28) |
11:00-12:59 |
79.97 ± 144.51 (n=93) |
0.68 ± 1.86 (n=93) |
13:00-14:59 |
159.41 ± 303.43 (n=61) |
1.74 ± 3.80 (n=61) |
15:00-16:59 |
65.40 ± 140.58 (n=35) |
1.16 ± 1.99 (n=35) |
Event and Action Plan
· It
is proposed that to take the response variables (clicking and whistling rates;
and the hours in peak occurrence at the two EAR sites) into account for
formulating the Action and Limit Levels of the Event and Action Plan:
· Departures
of any of these variables between baseline and construction phases with a 20%
difference will be of concern and should trigger the Action Level.
· Departures
of any of these variables between baseline and construction phases with a 40%
difference should trigger the Limit Level and immediate action will be
required.
· A
shift of 3 hours or more in peak occurrence at the bridge alignment area should
trigger the Action Level.
· A
shift of 6 hours or more in peak occurrence at the bridge alignment area should
trigger the Limit Level.
·
However, if there is a shift in peak occurrence
in both sites (Fan Lau and bridge alignment area), the action or limit level
should not be triggered, as the change in peak occurrence does not only occur
at the site of impact but also at the control site (Fan Lau), and the changes
in peak occurrences of dolphins at both sites may not be directly to the HKLR09
construction works.
·
The detailed Event and Action Plan is presented
in Table 8.2.
Table 8.2 Event
and Action Plan on Dolphin Movement and Behaviour
EVENT |
ACTION |
|||
ET Leader |
IEC |
SO |
Contractor |
|
Action
Level With the numerical values presented in Table 1, when
any of the response variable for dolphin acoustic behaviour
recorded in the construction phase monitoring is 20% lower or higher than that recorded in the baseline
monitoring, or when there is a shift of 3 hours or more in peak occurrence at B2 Site (i.e. 00:00 –
01:00), the action level should be triggered |
1. Repeat statistical data analysis to
confirm findings; 2. Review all available and relevant data
to ascertain if differences are as a result of natural variation or seasonal
differences; 3. Identify
source(s) of impact; 4. Inform the IEC, SO and Contractor; 5. Check monitoring
data; 6. Carry out audit to ensure all dolphin
protective measures are implemented fully and additional measures be proposed
if necessary |
1. Check monitoring data submitted by ET
and Contractor; 2. Discuss monitoring with the ET and the
Contractor; |
1. Discuss with the IEC the repeat
monitoring and any other measures proposed by the ET; 2. Make agreement on measures to be
implemented. |
1. Inform the SO and confirm notification
of the non- compliance in writing; 2. Discuss with the ET and the IEC and
propose measures to the IEC and the SO; 3. Implement the agreed measures. |
Limit
Level With the numerical values presented in Table 1, when
any of the response variable for dolphin acoustic behaviour
recorded in the construction phase monitoring is 40% lower or higher than that recorded in the baseline
monitoring, or when there is a shift of 6 hours or more in peak occurrence at
B2 Site (i.e. 00:00 – 01:00), the limit level
should be triggered |
1. Repeat statistical data analysis to
confirm findings; 2. Review all available and relevant data
to ascertain if differences are as a result of natural variation or seasonal
differences; 3. Identify
source(s) of impact; 4. Inform the IEC, SO and Contractor; 5. Check monitoring
data; 6. Carry out audit to ensure all dolphin
protective measures are implemented fully and additional measures be proposed
if necessary 7. Discuss additional dolphin monitoring
and any other potential mitigation measures (e.g. consider to temporarily
stop relevant portion of construction activity) with the IEC and Contractor. |
1. Check monitoring data submitted by ET
and Contractor; 2. Discuss monitoring with the ET and the
Contractor; 3. Review proposals for additional
monitoring and any other measures submitted by the Contractor and advise ER
accordingly. |
1. Discuss with the IEC the repeat
monitoring and any other measures proposed by the ET; 2. Make agreement on measures to be
implemented. |
1. Inform the SO and confirm notification
of the non- compliance in writing; 2. Discuss with the ET and the IEC and
propose measures to the IEC and the SO; 3. Implement the agreed measures. |
Abbreviations:
ET – Environmental Team, IEC – Independent Environmental Checker, SO –
Supervising Officer
8.4
Detailed methodology, results and discussion can
be found in the Dolphin Acoustic Behaviour Baseline Monitoring Report in Appendix H.