Contents
9.2 Legislation,
Standards and Guidelines
9.3 Methodology
for Baseline Establishment
9.4 Description of Existing Fisheries Baseline Conditions
9.5 Identification
and Evaluation of Impacts
9.8 Environmental Monitoring and Audit Programme
Figures |
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Current Status of Fish Ponds |
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Appendix |
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Photographs of Ponds in Assessment Area |
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9
Fisheries
Impact
9.1.1.1
This
Section of EIA presents the approach to and the findings of the fisheries
impact assessment based on the RODP shown in Figure 3.1.
9.1.1.2
The fisheries impact assessment has been prepared
in accordance with the EIA Study Brief No. ESB-246/2012 for the proposed
Project “Housing Sites in Yuen Long South” (hereinafter referred to as “the
Project”).
9.1.1.3
The Project for the purpose of EIA refers to the
planning and engineering feasibility study to review the development potential
of the Potential Development Area (PDA) in Yuen Long South with a view to
identifying housing sites for private and public housing developments and the
associated infrastructural works for the proposed developments. PDA refers to
the areas within the boundary of the proposed development design in Yuen Long
South, including the public and private housing developments and the
government, institution or community facilities and open space and/or
amenities.
9.1.1.4
The Assessment Area for fisheries impact assessment
as stipulated under Section 3.4.6 of the EIA Study Brief No. ESB-246/2012 shall
include all areas within 500m distance from the site boundaries of the Project
and shall be extended to include other areas if they are to be impacted by the
construction and operation of the Project during the course of the EIA
Study. Special attention shall be paid
to pond culture resources and activities as well as any watercourses which
serve as water sources for fish ponds.
9.1.1.5
The fisheries impact assessment has been conducted
in accordance with requirement of Annexes 9 and 17 of TM-EIAO as well as the
requirements set out under Section 3.4.6 and Appendix 7.7 of the EIA Study
Brief.
9.2
Legislation, Standards and Guidelines
9.2.1.1
The
relevant legislation, standards and guidelines applicable to the present study
for the assessment of fisheries impact include:
·
Environmental Impact Assessment Ordinance
(EIA Ordinance) (Cap. 499)
·
Water Pollution Ordinance (Cap. 358)
·
Fisheries Protection Ordinance (Cap. 171)
·
Marine Fish Culture Ordinance (Cap. 353)
·
The general criteria and guidelines for
evaluation and assessing fisheries impacts and considering mitigation measures
are documented in the Annexes 9 and 17 of the Technical Memorandum on
Environmental Impact Assessment Process (TM-EIAO)
9.3
Methodology
for Baseline Establishment
9.3.1
Literature
Review
9.3.1.1
A
desktop study was conducted to assess the baseline conditions of pond fish
culture activities and resources within the Assessment Area with respect to the
fisheries activities of Hong Kong as a whole. Information and literature
reviewed include:
·
AFCD Annual Reports (1997 – 2016);
·
AFCD website
(http://www.afcd.gov.hk/english/fisheries/fish_aqu/fish_aqu.html)
·
AFCD Accredited Fish Farm Scheme Website
(http://www.hkaffs.org/en/index.html)
·
EIA & TIA Studies for the
Stage 2 of PWP Item No. 215DS-Yuen Long and Kam Tin Sewerage and Sewage
Disposal (YLKTSSD) prepared by Ove Arup & Partners Hong Kong Ltd (2004)
(Ref. No. EIA-094/2004)
·
EIA for Hung Shui
Kiu New Development Area prepared by AECOM (2016) (Ref. No. EIA-248/2016)
·
AFCD’s internal
records of ponds
9.3.2
Site
Survey
9.3.2.1
Site
surveys were initially conducted during February 2013 and May 2013 to
investigate the actual status of fisheries and the conditions of fisheries
resources within the Assessment Area.
Additional surveys were conducted during March 2014 – April 2014 and
during September 2016 – May 2017 to verify the conditions of the ponds
identified at later stages as a result of the expansion of Assessment Area of
the RODP. All ponds within the
Assessment Area were identified and mapped on plan. Fisheries operation such as stocking, feeding
and harvesting, the presence of equipment or devices related to fisheries
operation, and signs of maintenance of fish pond bunds were recorded. Observations were also supplemented by any
fisheries-related activities observed during other field surveys for
terrestrial ecology. Photographs of the identified fish ponds were taken during
the surveys (see Appendix 9.1).
9.3.2.2
Based
upon observations during site surveys, ponds within the Assessment Area were
categorised as follows:
·
Active: ponds currently utilised for commercial
aquaculture activities; this category includes commercial fish ponds, fish fry
ponds and water flea ponds;
·
Inactive: no current commercial aquaculture
activities, but no major physical constraints to the resumption of such
activity in the short-term; this includes ponds with fish present in
non-commercial quantities and ponds used for casual sport fishing or for water
sports;
·
Abandoned: ponds in which there is physical evidence
that aquaculture has not taken place for many years (e.g. ponds overgrown with
vegetation) and/or where there are obvious physical constraints to the
resumption of fisheries activities (e.g. ponds that are fenced off and
inaccessible); ponds that are being utilised for non-fisheries related activities
and concreted ornamental/ landscaped ponds are also included in this category.
9.3.2.3
During
the site surveys, interviews with local villagers or fish farmers were conducted wherever
possible to obtain information about fisheries activities in the Assessment
Area.
9.4
Description of
Existing Fisheries Baseline Conditions
9.4.1
Review of Existing Information
9.4.1.1
Pond
fish culture has been centred in the north-west New Territories for decades.
Currently the majority (~96% in 2016) of local pond fish culture belong to
polyculture, with Bighead Carp Aristichthys
nobilis, Grass Carp Ctenopharyngodon
idellus, Common Carp Cyprinus carpio and Silver Carp Hypophthalmichthys molitrix in a
combination with Tilapia Oreochromis
spp. or Grey Mullet Chelon labrosus
being the most dominant culture species.
Approximately 4% of local pond fish culture belongs to monoculture of
carnivorous species such as Giant Groups Epinephelus
lanceolatus, Seabreams Acanthopagrus
spp. and Spotted Scat Scatophagus argus
in brackish fish ponds near to the coastline. Most of the fry and fingerlings
are imported from the Mainland and Taiwan, whilst some of the Grey Mullet fry
may also be captured from local coastal waters.
9.4.1.2
In
order to help local fish farms to develop, AFCD has launched the “Accredited
Fish Farm Scheme” (AFFS). Under this
scheme, products from registered fish farms are “accredited” by AFCD, and can
be marketed under the unique brand name of the scheme. Fish farms registered under the scheme will
be regularly inspected by AFCD officers, checking on the farm hygiene
conditions, the maintenance of management records, water quality and fish
health conditions. A series of advisory
leaflets and guidelines on aquaculture management, including “Good Aquaculture
Practices Series 3 – Environmental Management on Pond Fish Culture” and “Good
Aquaculture Practices Series 5 – Fry Health Management” have been published by
Aquaculture Fisheries Division of AFCD.
These publications provide guidelines on physical environment
requirements for establishment of fish pond farms, drainage requirements, water
quality, and a list of good fish pond culture practices for pond fisheries and
fry management.
9.4.1.3
According
to information from AFCD website, local inland ponds cover an area of
approximately 1,135ha, producing 2,092 tonnes of freshwater fish amounting to
$53million in 2016. Table 9.1 summarises the annual pond fish production and fish pond
area between 1997 and 2016 based on information extracted from AFCD annual
report and website.
Table 9.1 Annual Pond Fish Production
and Fish Pond Area
Year |
Pond Fish Production (tonnes) |
Fish Pond Area (ha) |
Overall Pond Fish Production Rate (kg/ha/year) |
1997 |
5000 |
1125 |
4444 |
1998 |
4900 |
1110 |
4414 |
1999 |
4500 |
1094 |
4113 |
2000 |
2817 |
1060 |
2657 |
2001 |
2550 |
1059 |
2407 |
2002 |
1989 |
1030 |
1931 |
2003 |
2114 |
1029 |
2054 |
2004 |
1977 |
1026 |
1927 |
2005 |
1897 |
1026 |
1849 |
2006 |
1943 |
1024 |
1897 |
2007 |
1927 |
1160 |
1661 |
2008 |
2266 |
1160 |
1953 |
2009 |
2105 |
1160 |
1814 |
2010 |
2190 |
1109 |
1975 |
2011 |
2315 |
1130 |
2049 |
2012 |
2306 |
1150 |
2005 |
2013 |
2187 |
1150 |
1902 |
2014 |
2001 |
1140 |
1755 |
2015 |
2092 |
1140 |
1835 |
2016 |
2543 |
1135 |
2241 |
9.4.2.1
A
total of 51 ponds were identified within or close to the Assessment Area as
listed in Table 9.2 below and their
locations and status are displayed in Figure 9.1. Photographs of each identified
ponds taken during site surveys are presented in Appendix 9.1. The locations and extent of
ponds were mapped on plan in Figure 9.1 based on the information from GeoInfo Map from Lands Department and
further verified through updated field surveys.
9.4.2.2
A
total of nine ponds identified within PDA, including five shallow farm ponds
(Ponds #5 - #9) near Sha Tseng Tsuen in Area 1, a small, managed shallow pond
(Pond #17) to the east of Lam Tai East Road in Area 2, two abandoned and
overgrown ponds (Ponds #23 and #24) located near the southern end of Kung Kum
Road, and an abandoned and dry pond (Pond #37) located near the southern end of
Long Hon Road in Area 1 of the PDA. All
the farm ponds (Ponds #5 – 9) in Area 1 within the PDA are shallow farm ponds
being used for irrigation. In the most
recent survey in 2016, Pond #17 was found containing very shallow water (not
suitable for fisheries purposes) and partially fenced. The pond appeared to be actively managed but
the use of this pond was uncertain.
There are some other farm ponds (Ponds #1, #10, #12, #13 and #42)
located in the Assessment Area but outside of the Project Area. These farm ponds are either ponds for
retention of rainwater for irrigation or inactive wet-fields for wet
agriculture.
9.4.2.3
There
are a total of four active fish ponds identified during the surveys, including
two small fish ponds/ managed ponds (Ponds #3 and #4) located behind the dense
woodland behind Shan Ha Tsuen and outside of the PDA. These two ponds were being operated by the
local villagers for cultivation of Nile Tilipia Oreochromis niloticus.
However, it is not certain if the fish are commercial fish stocks or for
self-consumption by the ponds’ owner(s). The remaining active fish ponds (Pond
#34 and #35) are located at about 700m to the Southeast of the southern end of
Kiu Hing Road and are located outside of the 500m Assessment Area. Fisheries-related equipment was seen at
nearby fishponds #34 and #35. However,
the scale of operations of these fishponds is small because of their small
sizes and isolated locations, making their nature and commercial uses
uncertain.
9.4.2.4
There
is an inactive fish pond (Pond #22) recorded near Fui Sha Wai outside of the
Project area.
9.4.2.5
There
are some ponds which are being actively disturbed/ managed for non-fisheries
related uses, including two Fung Shui Ponds/ Landscaped Ponds (Ponds #2 and
#21) of the local villages, seven stormwater ponds (Ponds #14, #16, #39, and
#48 - #51) which are largely concreted, four mitigation ponds (Ponds #43, #44,
#46 and #47), and some ponds which have recently been filled (Ponds #20, #28 -
#32, and #38). The remaining ponds
identified during surveys belong to abandoned ponds heavily overgrown with vegetation.
Table 9.2 Status of Ponds within Assessment Area
Pond Ref. No. |
Location |
Within PDA/
Project Area (Yes/ No) |
Status |
Area (ha) |
Remarks |
1 |
Near Yeung
Ka Tsuen |
No |
Abandoned |
0.18 |
Appeared to
be a former farm pond for irrigation |
2 |
Near Fui
Sha Wai |
No |
Abandoned |
0.16 |
Fung Shui
Pond/ Landscaped Pond |
3 |
~250m west
of southern end of Long Hon Road |
No |
Possibly
Active |
0.10 |
Actively
managed pond for cultivation of Tilapia; commercial use is uncertain |
4 |
~250m west
of southern end of Long Hon Road |
No |
Possibly
Active |
0.02 |
Actively
managed pond for cultivation of Tilapia; commercial use is uncertain |
5 |
Near Sha
Tseng Tsuen |
Yes |
Abandoned |
0.03 |
Active farm
pond (shallow pond) for irrigation |
6 |
Near Sha
Tseng Tsuen |
Yes |
Abandoned |
0.03 |
Active farm
pond (shallow pond) for irrigation |
7 |
Near Sha Tseng
Tsuen |
Yes |
Abandoned |
0.18 |
Active farm
pond (shallow pond) for irrigation |
8 |
Near Sha
Tseng Tsuen |
Yes |
Abandoned |
0.10 |
Active farm
pond (shallow pond) for irrigation |
9 |
Near Sha
Tseng Tsuen |
Yes |
Abandoned |
0.03 |
Active farm
pond for irrigation |
10 |
South of Shan
Ha Tsuen |
No |
Abandoned |
0.12 |
Appeared to
be a former farm pond for irrigation |
11 |
Within
woodland adjacent to Tan Kwai Tsuen Fresh Water Service Reservoir |
No |
Abandoned |
0.03 |
Abandoned
pond within woodland |
12 |
Near Fui
Sha Wai |
No |
Abandoned |
0.12 |
Active farm
pond (shallow pond) for irrigation |
13 |
Near Yeung
Uk Tsuen |
No |
Abandoned |
0.21 |
Appeared to
be a former farm pond for irrigation |
14 |
At Kiu Tau
Wai |
No |
Abandoned |
0.43 |
Stormwater
pond in Kiu Tau Wai Stormwater Pumping Station |
15 |
Near
Sheung Cheung Wai |
No |
Abandoned |
0.60 |
Marsh Pond |
16 |
Near
Sheung Cheung Wai |
No |
Abandoned |
0.63 |
Stormwater
pond in Sheung Cheung Wai Stormwater Pumping Station |
17 |
~80m
east of middle of Lam Tai East Road |
Yes |
Abandoned |
0.04 |
Managed pond
(shallow pond); nature and commercial use uncertain |
18 |
Near
Wong Nai Tun Tsuen |
No |
Abandoned |
0.05 |
Overgrown
pond next to a house |
19 |
Near
Tai Tong Tsuen |
No |
Abandoned |
0.17 |
Overgrown
pond |
20 |
Near
Yeung Ka Tsuen |
No |
Abandoned
& Filled |
0.31 |
Filled |
21 |
Near
Ying Lung Wai |
No |
Abandoned |
0.09 |
Fung Shui
Pond/ Landscaped Pond |
22 |
Near
Fui Sha Wai |
No |
Inactive |
0.25 |
Inactive
Fish Pond near Fui Sha Wai |
23 |
~300m
near the southern end of Kung Um Road |
Yes |
Abandoned |
0.12 |
Overgrown
with vegetation |
24 |
~300m
near the southern end of Kung Um Road |
Yes |
Abandoned |
0.05 |
Overgrown
with vegetation |
25 |
Near
Kong Tau Tsuen |
No |
Abandoned |
0.03 |
Overgrown
with vegetation |
26 |
Near
Kong Tau Tsuen |
No |
Abandoned |
0.02 |
Overgrown
with vegetation |
27 |
Near
Tai Kei Leng |
No |
Abandoned |
0.03 |
Overgrown
with vegetation |
28 |
Near
Tai Tong Tsuen |
No |
Abandoned
& Filled |
0.05 |
Filled |
29 |
Near
Tai Tong Tsuen |
No |
Abandoned
& Filled |
0.11 |
Filled |
30 |
Near
Tai Tong Tsuen |
No |
Abandoned
& Filled |
0.02 |
Filled |
31 |
Near
Tai Tong Tsuen |
No |
Abandoned
& Filled |
0.05 |
Filled |
32 |
Near
Tai Tong Tsuen |
No |
Abandoned
& Filled |
0.05 |
Filled |
33 |
~700m
near the southern end of Kiu Hing Road |
No |
Abandoned |
0.04 |
Overgrown
with vegetation |
34 |
~700m
near the southern end of Kiu Hing Road |
No |
Possibly
Active |
0.03 |
Managed fish
pond; commercial use uncertain |
35 |
~700m
near the southern end of Kiu Hing Road |
No |
Possibly
Active |
0.05 |
Managed
fish pond; commercial use uncertain |
36 |
Near
Yeung Ka Tsuen |
No |
Abandoned |
0.03 |
Overgrown
with vegetation |
37 |
Near
the southern end of Long Hon Road |
Yes |
Abandoned |
0.10 |
Dried out
and overgrown with vegetation |
38 |
Near
Tai Tong Tsuen |
No |
Abandoned
& Filled |
0.01 |
Filled |
39 |
At
Ma Tin Tsuen |
No |
Abandoned |
0.12 |
Stormwater
pond in Ma Tin Tsuen Stormwater Pumping Station |
40 |
~600m
northwest of San Sang San Tsuen |
No |
Abandoned |
0.13 |
Landscaped
Pond |
41 |
~600m
northwest of San Sang San Tsuen |
No |
Abandoned |
0.31 |
Overgrown
with vegetation |
42 |
~600m
northwest of San Sang San Tsuen |
No |
Abandoned |
0.21 |
Active farm
pond for irrigation |
43 |
~500m
north of San Sang San Tsuen under Western Corridor |
No |
Abandoned |
0.07 |
Mitigation
pond |
44 |
~500m
north of San Sang San Tsuen under Western Corridor |
No |
Abandoned |
0.08 |
Mitigation
pond |
45 |
~500m
north of San Sang San Tsuen under Western Corridor |
No |
Abandoned |
0.09 |
Overgrown
with vegetation |
46 |
~500m
north of San Sang San Tsuen under Western Corridor |
No |
Abandoned |
0.18 |
Mitigation
pond |
47 |
~500m
north of San Sang San Tsuen under Western Corridor |
No |
Abandoned |
0.13 |
Mitigation
pond |
48 |
At
Sik Kong Wai |
No |
Abandoned |
0.34 |
Stormwater
pond in Sik Kong Wai Stormwater Pumping Station |
49 |
At
Sik Kong Wai |
No |
Abandoned |
0.31 |
Stormwater
pond in Sik Kong Wai Stormwater Pumping Station |
50 |
At
Sik Kong Tsuen |
No |
Abandoned |
0.18 |
Stormwater
pond in Sik Kong Tsuen |
51 |
At
Lo Uk Tsuen |
No |
Abandoned |
0.32 |
Stormwater
pond next to Lo Uk Tsuen |
9.5
Identification and Evaluation of Impacts
9.5.1
Construction Phase – Direct Impacts
9.5.1.1
Potential
direct impacts on pond fisheries during construction phase could be resulted
from temporary or permanent loss of fish ponds or areas for fish pond operation
during construction of the Project. Of
the nine ponds identified within the PDA, a total of eight ponds (Ponds #5 -
#9, #17, #23 - #24) will be permanently lost due to the construction of the
Project. The five ponds (Ponds #5 - #9)
identified in the Area 1 of PDA are active farm ponds (near Sha Tseng Tsuen)
which are all shallow ponds for retention of water for irrigation purposes (or
inactive wet-fields for wet agriculture). The small, shallow pond located to
east of Lam Tai East Road in the Area 2 (#17) appeared to be actively managed
but it was too shallow for fisheries operation and the use of the pond was
uncertain. There are two overgrown and abandoned ponds (Ponds #23 and #24) in
Area 3 which will be permanently lost due to construction of the Project. The abandoned and dry pond (i.e. Pond #37)
located in Area 1 of PDA will be preserved in Green Belt (GB) zone in the
RODP. All the eight ponds namely Ponds
#5 - #9, #17 and #23 - #24 are considered as “Abandoned Fish Ponds” as they
have no historical records of fisheries-related uses. No active fish ponds will be lost due to the
Project. As the affected ‘abandoned fishponds’
are all small in size (ranging from 0.03ha to 0.18ha and approximately 0.58ha
in total), the direct fisheries impacts on pond fisheries/ aquaculture are
considered to be negligible when taking into account the potential that these
ponds are all resumed as active fish ponds for commercial fisheries operation.
9.5.2
Construction Phase – Indirect Impacts
9.5.2.1
Potential
sources for construction phase indirect impacts on pond fisheries include
impacts on bund stability, water seepage, blockage of access to fish ponds,
disruption of hydrology and deterioration of water quality or degradation of
the environmental conditions of the fish ponds.
9.5.2.2
The
only possibly active fish ponds that will be retained within 500m Assessment
Area are Ponds #3 and #4 located approximately 250m west of the southern end of
Long Hon Road, i.e. approximately 150m from the nearest boundary of Area 1 of
PDA. Given the long buffer distances of
these two possibly active fish ponds from the Project Area which is located at
the downstream, no significant indirect impacts arising from construction phase
of the Project resulting from degradation or deterioration of these two active
fish ponds are anticipated.
9.5.2.3
The
remaining ponds identified within 500m Assessment Area comprise mainly
abandoned and overgrown ponds, and an inactive fish pond. With good site practices and proper control
of construction site run off, sewage discharge from work force, other sources of construction waste waters and accidental spillage as detailed in Section 6, the induced water quality impact as a result of deterioration of
water quality or degradation of the environmental conditions of fish ponds is
considered to be low.
9.5.3
Operational Phase – Direct Impacts
9.5.3.1
The
Project will result in permanent loss of eight abandoned ponds with no signs of
fisheries-related uses (Ponds #5 – 9, #17, #23 and #24) within the PDA. The impact of loss of these ponds has been
evaluated under Section 9.5.1. No other direct impacts during operational
phase of the Project are anticipated.
9.5.4
Operational Phase – Indirect Impacts
9.5.4.1
Potential
sources of indirect impacts on pond fisheries during operational phase of the
Project may include blockage of access to active fishponds, and degradation/
deterioration of environmental conditions of fish ponds due to induced-water
quality impacts from sewage and runoff from the proposed development. As the only two possibly active fish ponds
(Ponds #3 and #4) that will be retained within the 500m Assessment Area are
located in upstream area and at long buffer distances from the Project Area, no
significant indirect impacts resulting from degradation of the environmental
conditions of or blockage of access to these active fish ponds are anticipated
during operation of the Project. In
addition, the Project will provide an sewage treatment works and associated
sewerage facilities to serve the proposed development. It is expected that during the operational phase of
the Project, sewage and domestic discharge within the PDA will be properly
collected and treated as detailed in Sections
6 and 7. As such, no significant
indirect impacts as a result of degradation of the environmental conditions of
existing or potential fish ponds (i.e. inactive/ abandoned ponds that could be
resumed for fisheries operation) are anticipated during the operational phase of
the Project.
9.5.5
Cumulative Impacts
9.5.5.1
As
the Project is not expected to result in any significant direct or indirect
impacts on pond fisheries during construction and operational phases of the
Project, no significant cumulative impacts arising from concurrent projects on
pond fisheries are anticipated.
9.6.1.1
As
no significant impacts arising from construction and operational phases of the
Project on pond fisheries are anticipated, no mitigation measures on fisheries
are required. However, the good site practices for the control of construction
site runoff as detailed in Section 6
shall be fully implemented to minimise impacts on water sources for potential
sites for pond fish culture in the Project Area or its vicinity.
9.7.1.1
With
proper good site practices implemented during construction phase, no residual
impacts on pond fish culture are anticipated.
9.1
Environmental
Monitoring and Audit Programme
9.1.1.1
No
significant fisheries impacts are anticipated from the construction phase and
operation phase of the Project. Hence,
the formulation and the implementation of an environmental monitoring and audit
programme for assessing the impacts on fisheries resources and fisheries
operation is not considered necessary. However,
good site management during construction phase as mentioned in Section 6 will be implemented so that
the treated runoff will be discharged to public drainage system in compliance
with the WPCO.
9.2.1.1
A
comprehensive review of the status of pond fish culture has been conducted
through desktop study and field surveys to establish the fisheries baseline of
the Assessment Area, with the assessment of fisheries conducted in accordance
with the TM-EIAO requirements.
9.2.1.2
Of
the total 51 ponds identified in the Assessment Area, only nine ponds were
identified within PDA. These include
five shallow farm ponds for irrigation (Ponds #5 - #9) near Sha Tseng Tsuen in
Area 1, a small, shallow pond appeared to be actively managed with uncertain
use (Pond #17) located to near the southern end of Lam Tai East Road in Area 2,
two abandoned and overgrown ponds (Ponds #23 and #24) located near the southern
end of Kung Kum Road, and an abandoned and dry pond (Pond #37) located near the
southern end of Long Hon Road in Area 1 of the PDA. Of these nine ponds identified in PDA, only
the abandoned and dry pond (Pond #37) in Area 1 will be preserved in the
proposed Green Belt (GB) zone in the RODP.
The remaining eight ponds will be lost due to the Project. As all the eight ponds to be lost within the
PDA serving non-fisheries related purposes (of approximately 0.58ha in total)
are small in overall area, the direct fisheries impacts on pond fisheries/
aquaculture are considered to be negligible when taking into account the
potential that these ponds are all resumed as active fish ponds for commercial
fisheries operation.
9.2.1.3
With
the separation distances (~150m) from the nearest boundary of the PDA, no
direct or indirect impacts on the two possibly active fishponds (Ponds #3 and
#4) are anticipated during the construction and operational phases of the
Project. As such, no fisheries
mitigation measures are considered necessary. In addition, the Project will
provide a sewage
treatment works and associated sewerage facilities to serve the proposed
development. It is expected that during the operational phase of
the Project, sewage and domestic discharge within the PDA will be properly
collected and treated as detailed in Sections
6 and 7. As such, no significant indirect impacts as a
result of degradation of the environmental conditions of existing or potential
fish ponds (i.e. inactive / abandoned ponds that could be resumed for fisheries
operation) are anticipated during the operational phase of
the Project.
9.2.1.4
With
the full implementation of the good site practices to control sewage discharge
and site runoff as detailed in Section 6,
no adverse induced water quality impacts on water sources for potential fish
pond sites are anticipated.
AFCD Annual Reports (1997 – 2016) (http://www.afcd.gov.hk/english/publications/publications_dep/publications_dep.html) visited in May 2017.
AFCD website
(http://www.afcd.gov.hk/english/fisheries/fish_aqu/fish_aqu.html) visited in May 2017.
AFCD Accredited Fish Farm Scheme Website
(http://www.hkaffs.org/en/index.html)
downloaded on 18th February 2014.