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INTRODUCTION
The Laguna Lake
Development Authority has been in place since 1966 (Republic Act no.
4850) and since 1975 has been given the primary responsibility to
promote the development of the Laguna de Bay region, while providing
for environmental management and control, preservation of the
quality of life and ecological systems, and the prevention of undue
ecological disturbance, deterioration and pollution.
Since the early
seventies LLDA has been regularly conducting water quality
monitoring of the Laguna de Bay and its tributaries. These routine
monitoring activities have been made part of the LLDA program
especially when assessing the status of the lake under different
circumstances.
The objectives of
the routine LLDA water quality monitoring programs are:
-
To accurately
assess the suitability of the lake for all its present and
intended beneficial uses;
-
To evaluate the
impacts of development activities on the lake’s water quality
that will serve as important criteria for environmental planning
and management.
Routine monitoring
programs conducted by LLDA cover different locations, time periods
and parameters. However, considering the vast area of Laguna de Bay
and the high costs involved, these monitoring programs will
inevitably be limited in their coverage, both spatially and
temporally.
With the recent
set-up of an information system for storage, processing and analysis
of environmental data (HYMOS), the presentation of the routine
monitoring data can now be automated and further improved. To
present the water quality status of the lake and its tributaries on
a monthly basis, a Mondriaan-like presentation was developed dubbed
the ‘Water Mondriaan’. Its purpose is to provide the policy making
body of the authority as well as the various stakeholders through
the LLDA website, an immediate and comprehensive overview on
selected characteristic water quality parameters at different parts
of the water system without suggesting to have detailed spatial
information.
The Water Mondriaan
is a schematic map of the Laguna de Bay water system, showing the
monitoring results in the lake and its tributaries compared with the
DENR water quality criteria/water usage & classification for
freshwater systems or when absent the LLDA expert opinion. The
parameters included, focus on factors of significant ecological,
human health and resource use importance or on the processes that
are crucial to them:
-
oxygen and
oxygen demand (%DO, BOD5 and COD)
-
bacterial
pollution (Total Coliforms, Fecal Coliforms)
-
eutrophic level
(phosphate, dissolved nitrogen, chlorophyll-a and phytoplankton
abundance)
-
hazardous
substances (oil & grease and on a quarterly basis lead,
hexavalent chromium and cadmium)


MONITORING PROGRAMS
Routine monitoring
of the water quality of the lake and its tributaries has been in
place since 1973. In time, the program has been slightly adjusted
regarding spatial and temporal coverage and the number of parameters
included. In the figure and table below the present lake and
tributary monitoring stations are presented.
* position your cursor
over a point to see the location of the station

Assuming that the
stations are indicative of their immediate surroundings an overall
schematic impression of the water quality status can be obtained.
Results will be presented on a monthly basis in a schematized
Mondriaan-like representation of the Laguna de Bay as shown in the
figure below.


SELECTED PARAMETERS
Oxygen saturation and oxygen demand
The
oxygen saturation level indicates the degree of pollution by organic
matter, the level of primary production and the level of self
purification of the water. The BOD5 expresses the oxygen demand for
the biodegradation of organic matter and indicates the risk for low
DO saturation levels. Almost 70% of BOD5 loads in the Laguna de Bay
are from households and 20% is from industrial origin: the remaining
part is from land run-off. COD expresses the total oxygen demand,
including the oxidation of all organic matter and reduced inorganic
compounds as ammonium. In shallow lakes, excessive BOD5 and COD can
cause oxygen depletion and suffocate living resources.
Bacterial pollution
Ideally, a water
system should not contain any micro-organisms known to be pathogenic
or any bacteria indicative of faecal pollution as it would render
the water unsuitable for all sorts of functions. The existence of
these micro-organisms can be linked to untreated sewage and sludges,
night soil and animal wastes. Exposure to human pathogens via
contact with contaminated water or consumption of contaminated
shellfish can result in infection and disease. Selected indicator
parameters are Total Coliforms and Fecal Coliforms, as these two
have been used in the DENR water quality criteria / water usage &
classification for freshwater systems.
Eutrophic level
Perhaps the most
pressing problem in Laguna de Bay is eutrophication or nutrient
enrichment from domestic (some 70 – 80%), agricultural and to a
lesser extent from industrial loads. Excessive levels of nutrients
such as dissolved nitrogen and phosphate (o-PO4P) increase primary
production. At adverse levels, impacts include nuisance algal blooms
and oxygen depletion, which suffocate living resources. In addition,
total phytoplankton cell counts and chlorophyll-a are presented. The
net primary production is also given in relation to the potential
fish production in the lake. Phytoplankton refers to microscopic
aquatic plants that have a very significant role in aquatic
productivity because it provides food and oxygen necessary for the
survival of aquatic animals. Chlorophyll-a is the photosynthetic
pigment that relates to the total phytoplankton biomass. Phosphate
is the only selected parameter that is used in the DENR water
quality criteria / water usage & classification for freshwater
systems.
Hazardous substances
Hazardous
substances, dissolved or suspended in the water column or
accumulated in sediments can result in an array of adverse
ecological effects. Many of these compounds are suspected
carcinogens and/or reproductive toxicants, which can accumulate on
the tissue of fish and shellfish, which may then be consumed by
humans. The bio-accumulative effects of these compounds on the
ecosystem depend on the characteristics of the compound. The three
most toxic heavy metals of the LLDA monitoring program were
selected: Hexavalent Chromium – Cr(6+), lead - Pb and Cadmium - Cd.,
all expressed as total concentration in the water phase
Hexavalent chromium
is used extensively in metal pickling and plating operations,
leather industry as tanning agent and in manufacturing paint and
dyes.
Mixed lead and zinc
ores account for about 70% of total primary lead production. Lead is
also produced from scrap (secondary lead), which accounts for about
35% of the total world lead supply. The largest consumer of lead is
the use as an additive in fuels, production of batteries, paints,
anti-radiation armour, pesticide formulation, pigments, cable
sheeting, alloys and various semi manufacturers.
Cadmium is a trace
element in the earth’s crust, which is generally associated with
zinc minerals. Cadmium and cadmium compounds are used mainly in
nickel / cadmium batteries, as bright yellow pigments in paints and
synthetic materials and as stabilizers of synthetic materials.
Furthermore, it can be produced as by-product of fertilizer,
application and waste-incineration industries.
Oil & grease was
selected as it may harm aquatic life by direct contact, by poisoning
with various water soluble substances, that may be leached from it
or by emulsions which may coat the fish gills or may be swallowed
with water and food.

PRESENTATION
The colours in the
Water Mondriaan (blue, white, yellow, red, black and grey) represent
the specific condition of the water system for a certain period with
respect to the selected parameters.
The selected colouring and other
details are indicated in the legends, which are specific to each
figure. The legends follow the DENR classification for freshwater
systems. When classes are described by the same water quality value,
they are merged and presented as one colour.
|
Classification |
User
Function |
| |
A |
Public Water Supply II |
| |
B |
Recreation I |
| |
C |
Fisheries, recreation
II and industrial water supply I |
| |
D |
Agriculture and
industrial water supply II |
| |
> D |
|
| |
No Data |
|
For the other
parameters (COD, pathogens, chlorophyll-a, phytoplankton abundance)
that cannot be presented through the DENR classification, the legend
reflects the LLDA expert opinion and will be expressed in terms of
‘very low’, ‘low’, ‘medium’, ‘high’ and ‘very high’.
The internet
provides a powerful tool for sharing and communicating information
and will be used to inform the stakeholders on the monthly
monitoring results. These results are available through the LLDA
website www.llda.gov.ph.
Moreover, in the
annual report, which will also be presented on the website, the
overview of monthly statements will be incorporated.

SELECTED CLASSIFICATION
|
BOD5 |
| |
class A/B |
<= 5 |
mg/l |
| |
class C |
> 5 - 10 |
mg/l |
| |
class D |
> 10 - 15 |
mg/l |
| |
worse than D |
>15 |
mg/l |
| |
No Data |
|
|
|
|
|
Chlorophyll-a |
| |
very low |
<= 25 |
ug/l |
| |
low |
> 25 - 50 |
ug/l |
| |
medium |
> 50 - 100 |
ug/l |
| |
high |
> 100 - 150 |
ug/l |
| |
very high |
> 150 |
ug/l |
| |
No Data |
|
|
|
|
%DO |
| |
class A/B |
<= 70 |
mg/l |
| |
class C |
60 - < 70 |
mg/l |
| |
class D |
40 - <60 |
mg/l |
| |
worse than D |
< 40 |
mg/l |
| |
No Data |
|
|
|
|
|
Phytoplankton |
| |
very low |
<= 1,000 |
cells/ml |
| |
low |
> 1,000 - 3,000 |
cells/ml |
| |
medium |
> 3,000 - 5,000 |
cells/ml |
| |
high |
> 5,000 - 10,000 |
cells/ml |
| |
very high |
> 10,000 |
cells/ml |
| |
No Data |
|
|
|
|
COD |
| |
very low |
<= 10 |
mg/l |
| |
low |
> 10 - 25 |
mg/l |
| |
medium |
> 25 - 50 |
mg/l |
| |
high |
> 50 - 75 |
mg/l |
| |
very high |
> 75 |
mg/l |
| |
No Data |
|
|
|
|
|
Oil and grease |
| |
class A/B |
<= 1 |
mg/l |
| |
class C |
> 1 - 2 |
mg/l |
| |
class D |
> 2 - 5 |
mg/l |
| |
worse than D |
> 5 |
mg/l |
| |
No Data |
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Total Coliforms 1 |
| |
class A/B |
<= 1,000 |
MPN/100ml |
| |
class C |
> 1,000 - 5,000 |
MPN/100ml |
| |
worse than C |
> 5,000 |
MPN/100ml |
| |
No Data |
|
|
|
|
|
Lead |
| |
class A/B/C |
<= 0.05 |
mg/l |
| |
class D |
> 0.05 - 0.5 |
mg/l |
| |
worse than D |
> 0.5 |
mg/l |
| |
No Data |
|
|
|
|
Fecal Coliforms 1 |
| |
class A |
<= 5 |
MPN/100ml |
| |
class B |
> 5 - 10 |
MPN/100ml |
| |
worse than B |
> 10 - 15 |
MPN/100ml |
| |
No Data |
|
|
|
|
|
Chromium (IV) |
| |
class A/B/C |
<= 0.05 |
mg/l |
| |
class D |
> 0.05 - 0.1 |
mg/l |
| |
worse than D |
> 0.1 |
mg/l |
| |
No Data |
|
|
|
|
Dissolved Nitrogen |
| |
very low |
<= 0.3 |
mgN/l |
| |
low |
> 0.3 - 1.0 |
mgN/l |
| |
medium |
> 1.0 - 3.0 |
mgN/l |
| |
high |
> 3.0 - 10.0 |
mgN/l |
| |
very high |
> 10.0 |
mgN/l |
| |
No Data |
|
|
|
|
|
Cadmium |
| |
class A/B/C |
<= 0.05 |
mg/l |
| |
class D |
> 0.05 - 0.5 |
mg/l |
| |
worse than D |
> 0.5 |
mg/l |
| |
No Data |
|
|
|
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Phospate |
| |
class A |
<= 0.1 |
mgP/l |
| |
class B |
> 0.1 - 0.2 |
mgP/l |
| |
class C |
> 0.2 - 0.4 |
mgP/l |
| |
worse than C |
> 0.4 |
mgP/l |
| |
No Data |
|
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1
geometric mean for a period of three months |
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