Scope of the monitoring programme
The EPD monitors the entire breadth of Hong Kong's
marine waters, collecting water and sediment samples from a number
of designated locations (monitoring stations) in the sea that are
identifiable by specific longitude and latitude co-ordinates. In
2005, it collected samples once a month from each of the 76 water
quality monitoring stations and twice a year from the 45 bottom
sediment sampling stations. In addition, it took further samples
from 18 water and 15 sediment stations covering the Government Dockyard
and 16 typhoon shelters and marinas across Hong Kong. At 25 of the
water quality monitoring stations in nine Water Control Zones, the
EPD also carried out monthly phytoplankton monitoring.
[Photo of The 76 marine monitoring stations in Hong Kong ]
The number of stations used to monitor water
quality has remained fairly stable since 1986, when there were 77
stations in use. However, in 1986 the EPD only had 19 bottom sediment
sampling stations, and has added a further 26 over the following
two decades. It also only monitored 13 typhoon shelters in 1986,
against the current total of 17 including the Government Dockyard.
The increases arose because two typhoon shelters (To Kwa Wan and
Hebe Haven) were added to the monitoring programme, as was a brand
new typhoon shelter at Hei Ling Chau and the new Government Dockyard
which were commissioned in 2000. The EPD collects water samples
bimonthly from the water quality monitoring stations in typhoon
shelters and the Government Dockyard, and twice a year from the
sediment stations.
Resources and equipment
[Photo of The general-purpose vessel
"Chop Yat" used in the early years]
Aside from the typhoon shelters, almost all
the monitoring stations are sited away from shore. This means that
the EPD relies on a dedicated monitoring vessel to access the stations
and obtain samples. From 1986 to 1992 it used a small general-purpose
vessel named the 'Chop Yat', supplemented as necessary by
hired boats and a Police Boat for sampling in the Deep Bay area.
As a general-purpose vessel, the 'Chop Yat' suffered from
having limited deck space, no cold room for storing samples, and
no on-board facilities for on-site analysis of samples. In 1993,
the EPD built a new vessel called the 'Dr. Catherine Lam' especially designed for monitoring in Hong Kong waters. Its namesake
Dr. Catherine Lam was active in the early years of setting up the
EPD's marine monitoring programme, and carried out valuable work
on phytoplankton and red tides. She was also instrumental in the
acquisition of the new monitoring vessel. Sadly, in 1990 Dr. Lam
passed away without seeing the project's completion, and the vessel
was named in her memory.
[Photo of The EPD's dedicated marine
monitoring vessel "Dr. Catherine Lam"]
The 'Dr. Catherine Lam' is operated
and maintained by the Marine Department, which also supplies its
crew. The vessel comes with adequate deck space, a built-in cold
room and in-house laboratory, and an inflatable boat for special
operations. The vessel was fitted with Global Positioning System
(GPS) technology, which was later upgraded to Differential Global
Positioning System (DGPS), allowing highly accurate positional readings
for locating monitoring stations. On deck, CCTV cameras are installed
to provide staff working on board with extra safety and security.
Electronically controlled cranes/winches have been installed on
the sides of the vessel to lower the heavy water/sediment sampler
and instruments into the water.
[Photo of Water monitoring in the 1980s]
In 1986 and right through to 1993, EPD personnel
took water samples manually by lowering a Van Dorn sampler into
the water at each monitoring station. These samples were then measured
by individual meters on deck for parameters such as temperature,
salinity and dissolved oxygen. The data was recorded by hand onto
paper forms
From 1994, the meters for in situ measurements
were replaced by a multiparameter "conductivity-temperature-depth"
(CTD) water quality profiler. As they were lowered into the water,
these new instruments measured parameters such as temperature, salinity,
dissolved oxygen and turbidity at different depths, thus obtaining
a vertical profile of the water column. The data from these instruments
was stored directly into a computer. These advanced pieces of equipment
enabled measurements to be made more quickly, efficiently and accurately.
In 1999, the EPD also replaced its hand-held Van Dorn water samplers
with a computer-controlled rosette water sampler. This new equipment
collects up to 12 water samples at once, and takes measurements
of physico-chemical parameters the same time as it collects the
samples. Today, the sampling procedure involves both the rosette
sampler and the CTD profiler being lowered into the water together
by electronic winch.
[Photo of A CTD meter and a water quality profiler housed within the rosette sampler]
Since 1995, all the data collected from water
sampling has been entered into the EPD's comprehensive Water Quality
and Pollution Load Information System (WQPLIS). This compact but
high-performing computer database system allows multiple modes of
data storage organisation and analysis, and makes data and trends
quickly available as required.
Trialled equipment
The EPD has always been ready to embrace new
technology that can help streamline and improve its water quality
monitoring programme. However, some promising new technology has
not been adopted, following trials to see how well it would suit
Hong Kong conditions.
One such piece of new technology was remote
sensing using telemetric monitoring. This was a development that
could allow for continuous monitoring of marine water quality by
stationing instruments at fixed marine sites. The instrument buoys
could electronically transmit data back to a base site, continuously.
By contrast, the EPD's existing programme required monthly visits
by staff to take individual samples.
[Photo of Telemetry Marine Water
Quality Monitoring System]
In 1996, the EPD began a seven-month trial of
an experimental Telemetry Marine Water Quality Monitoring System
(TMWQMS), to see how feasible it would be to deploy telemetric monitoring
in Hong Kong's marine waters. The trial certainly indicated that
the equipment was accurate in its readings. Problems, however, were
manifold. Costs of installing and maintaining the system were high,
but the system could only be placed at one or two sampling locations
and could not provide the territory-wide coverage required by a
comprehensive monitoring programme. It was prone to malfunction,
requiring regular repairs in addition to standard maintenance work.
In particular, it was quickly affected by biofouling (e.g. growth
of marine organisms on the equipment), which affected the functioning
of the sensors. Because it was left unattended for long periods
in the sea, the system was also vulnerable to vandalism, theft,
or the effects of storms or large waves. Finally, the system only
measured a limited number of parameters, reducing its effectiveness.
For reasons of usefulness and cost, therefore, the EPD decided not
to pursue telemetry for routine marine monitoring.
Sampling techniques
To collect water samples, EPD staff aboard
the monitoring vessel first have to locate the position of each
sampling station. In the 1980s, the positioning was determined visually
by reference to distinctive objects such as prominent landmarks
or nearby buoys. With the arrival of the new vessel 'Dr. Catherine
Lam' in 1993, the exact positions of monitoring stations could
be determined using the Global Positioning System aboard, later
upgraded to the even more precise Differential Global Positioning
System (DGPS). This system enables the vessel to be brought to within
one metre of the designated station position on every visit.
[Photo of EPD staff collecting water samples]
As mentioned above, in the early years individual
water samples were collected manually. Samples from different depths
would thus have to be taken separately, with one sample taken at
each depth. To obtain a comprehensive picture of the water body,
water samples at each station are generally collected from three
depths: one from one metre below the surface of the water ('Surface'),
one from midway between the surface and the sea bed ('Middle'),
and one from one metre above the sea bed ('Bottom'). With the introduction
of the rosette sampler in 1999, samples could be taken by a single
piece of equipment from all three depths in one haul.
For sediment sampling, EPD staff use sampling
grabs to collect sediment from the top 10cm of the seabed. The kind
of sediment grab used at each station depends on the depth of the
seabed there and the amount of sediment needing to be collected.
The EPD uses three different types of sediment grabs: a Birge-Ekman
grab (0.023sq.m.) for swallow water, a Van Veen grab (0.1sq.m.),
and a Smith-Mcintyre grab (0.1 sq.m.) for deeper water.