Opentopia Directory Encyclopedia Tools

Laguna de Bay

Encyclopedia : L : LA : LAG : Laguna de Bay


Laguna de Baý is the largest lake in the Philippines and the largest inland freshwater lake in Southeast Asia. It is located in the island of Luzon between the provinces of Laguna to the south and Rizal to the north. Metro Manila lies on its western shore. Its surface area is 949 square kilometers and has an average depth of only about 2 meters.

The lake is shaped like a stylized 'W', with two peninsulas jutting out from the northern shore. Laguna de Bay drains to Manila Bay through the Pasig River. The lake is filled with fish pens installed by fishermen who regularly fish there.

There are three islands in the lake, Talim island, which is a part of the towns of Binangonan and Cardona in Rizal province, Calamba island, privately-owned and developed into the posh Resort of Calamaba Island, and Los Baños island.

Laguna de Bay is the Old Spanish term for Lake of Bay. Bay (pronounced as bä'ï) is a town in Laguna province. Pulilan is the prehispanic name of the lake according to the 1613 Vocabulario de Lengua Tagala printed in Pila, Laguna.

Facts about the lake

The Laguna Lake is a large shallow freshwater body in the heart of Luzon Island, Philippines with an aggregate area of 91,136 hectares and a shoreline of 220 kilometers. The lake is fed by 45,000 square kilometers of catchment areas and its twenty one major tributaries. It is considered to be the second largest inland body of water in Southeast Asia, after Indonesia’s Lake Toba in Sumatra (Guerrero & Calpe, 1998). It is bordered by the province of Laguna in the east, west and southwest, the province of Rizal in the north to northeast, and Taguig, Pateros, Pasig and Marikina (all of which are cities and municipalities in Metropolitan Manila) in the northwest. The lake has an average depth of 2.8 meters and its excess water is discharged through the Pasig river. The southern and eastern portions of Metro Manila occupy a huge portion of its watershed (Gonzales, 1987; Guerrero & Calpe, 1998).

Currently, the lake serves as a multipurpose resource. It is a navigational lane for passenger boats, source of water for a nearby hydroelectric power plant, food support for the growing duck industry, aquaculture, recreation, fishery, flood control, source of irrigation water and a “virtual” cistern for domestic, agricultural and industrial effluents (Gonzales, 1987). Because of its importance in the development of the Laguna de Bay Region , unlike in other lakes in the country, its water quality and general condition are closely monitored (Department of Environment and Natural Resources, 1996). This important water resource has been greatly affected by development pressures like population growth, rapid industrialization, and resources allocation (Batu, 1996).

Government data showed that about sixty percent of the estimated 8.4 million people residing in the Laguna de Bay Region discharge their solid and liquid wastes indirectly to the lake through its tributaries. A large percentage of these wastes are mainly agricultural while the rest are either domestic or industrial (DENR, 1997). According to DENR (1997), domestic and industrial wastes contribute almost equally at thirty percent each. Meanwhile, agricultural wastes take up the remaining forty percent. In a recent sensitivity waste load model ran by the Laguna Lake Development Authority’s (LLDA) Integrated Water Resources Management (IWRM) Division, it revealed that 70 percent of Biochemical Oxygen Demand (BOD) loadings came from households, 19 percent from industries, 19 percent from industries, and 11 percent came from land run-off or erosion (LLDA, 2005).

As far as industries and factories are concerned, there are about 1,481 and is expected to increase over time (Guerrero & Calpe, 1998). Of the said figure, about 695 have wastewater treatment facilities. Despite this, the lake is absorbing huge amounts of pollution from these industries in the forms of discharges of industrial cooling water, toxic spills from barges and transport operations and hazardous chemicals like lead, mercury, aluminum and cyanide (Sly, 1984). Based from the said figure, sixty five percent are classified as “pollutive” industries.

The hastened agricultural modernization throughout the region took its toll on the lake. This paved the way for massive and intensified use of chemical based fertilizers and pesticides whose residues eventually find their way to the lake basin. These chemicals induce rapid algal growth in the area that depleted oxygen levels in the water. Hence, oxygen available to the lake is being used up thereby depleting the lake of available oxygen for the fish causing massive fish kills (Solidarity for People’s Power, 1992). As far as domestic wastes are concerned, around ten percent of the 4,100 metric tons of waste generated by residents of Metro Manila are dumped into the lake. As reported by the now defunct Metropolitan Manila Waterworks and Sewerage System (MWSS), only 15 percent of the residents in the area have an effective waste disposal system. Moreover, around 85 percent of the families living along the shoreline do not have toilets (SPP, 1992; Batu, 1996).

Because of the problems facing and threatening the potential of the lake, the then President Ferdinand Marcos signed into law Republic Act (RA) 4850 otherwise known as the law creating LLDA. The LLDA is the main agency tasked to oversee the programs that aimed to develop and protect the Laguna Lake. Though it started as a mere quasi–government agency with regulatory and proprietary functions, its charter was strengthened by Presidential Decree (PD) 817 in 1975 and by Executive Order (EO) 927 in 1983 to include environmental protection and jurisdiction over the surface waters of the lake basin. In 1993, by virtue of the devolution, the administrative supervision of the LLDA was transferred to the DENR by EO 149 (LLDA, 1994).

Environmental fee user system

To realize the objectives of the creation of LLDA, the agency implemented policies to curb down the possibility of stressing the lake’s assimilative capacity . The most recent policy was the Environmental User Fee System (EUFS). The EUFS was implemented by virtue of LLDA Board Resolution 22 in 1996. The objective of the policy was to “…(reduce) the pollution loading in to the Laguna de Bay by enjoining all discharges of liquid wastes to internalize the cost of environmental degradation…”. Formally, the said board resolution aptly defined the EUFS as a “market–based” policy instrument aimed at reducing the pollution loading in the lake. As such, companies found to have unusually high concentration of pollutants in their emissions, need to pay fines or lake “user – fees”.

The system is a market – based instrument that encourages companies to invest in and operate pollution prevention and/or abatement systems within their establishment. Applying the "Polluter Pay Principle", the system effects direct accountability for damage inflicted on the integrity of Laguna de Bay Region thereby encouraging individuals and business establishments to internalize into their decision-making process the environmental impacts of their day-to-day activities. The EUFS covers all enterprises within the administrative jurisdiction of LLDA that discharge wastewater in the Laguna de Bay system. These include commercial and industrial establishments; agro-based industries and establishments (such as swine farms and slaughterhouses); clustered dwellings (i.e. residential subdivisions); and domestic households (LLDA, 2001).

Under the EUFS, a firm is required to secure a discharge permit which is renewed on an annual basis at the LLDA. The discharge permit effectively allows the firm to discharge its wastewater to the lake or through its main tributaries. The discharge permit gives the establishment a legal right to dispose their waste water in the Laguna de Bay Region. Wastewater is basically, sewage, storm water and water used for various purposes around the community, including firms. Wastewater can either be domestic or non domestic. Domestic wastewater includes black water, or wastewater from toilets, and gray water, which is wastewater from all sources except toilets. Black water and gray water have different characteristics, but both contain pollutants and disease-causing agents that require monitoring. Non domestic wastewater are generated by offices, businesses, department stores, restaurants, schools, hospitals, farms, manufacturers, and other commercial, industrial, and institutional entities. Storm water is a nonresidential source and carries trash and other pollutants from streets, as well as pesticides and fertilizers from yards and fields (Taylor, et al, 2005).

According to the Clean Water Act of 2004, the DENR (through the LLDA) shall “implement a wastewater charge system in all management areas including the Laguna Lake region and Regional Industrial Centers through the collection of wastewater charges/fees. The system shall be established on the basis of payment to the government for discharging wastewater into the water bodies. Wastewater charges shall be established taking into consideration the following: a) to provide strong economic inducement for polluters to modify their production or management processes or to invest in pollution control technology in order to reduce the amount of water pollutants generated; b) to cover the cost of administering water quality management or improvement programs, including the cost of administering the discharge permitting and water pollution charge system; c) reflect damages caused by water pollution on the surrounding environment, including the cost of rehabilitation; d) type of pollutant; e) classification of the receiving water body; and f) other special attributes of the water body”.

The technical aspect regarding the quality of wastewater is given in DENR Administrative Order 1990-35. The order defines the critical water parameters’ value versus the classification of the body of water (e.g. lake or river). Discharge permits are issued by the LLDA only if the wastewater being discharged complied with the said order.

The EUF is a fee that is paid for the amount of pollution that is discharged into the tributary rivers within the Laguna de Bay Region. It is composed of a fixed fee and a variable fee. The fixed fee covers the administrative cost implementing the Environmental Users Fee System and is based on the volume of wastewater that is discharged.

According to LLDA Board Resolution 33, as amended, the fixed fee is different for those firms which discharge wastewater without or with heavy metals. The term heavy metal refers to any metallic chemical element that has a relatively high density and is toxic or poisonous at low concentrations. Examples of heavy metals include mercury (Hg), cadmium (Cd), arsenic (As), chromium (Cr), thallium (Tl), and lead (Pb).

Wastewater without heavy metals:
Fee Volume of Wastewater Discharge
Php 24,000 More than 150 cubic meters per day
Php 16,000 Between 30 and 150 cubic meters per day
Php 8,000 Less than 30 cubic meters per day

Wastewater with heavy metals:
Fee Volume of Wastewater Discharge
Php 12,000 Less than 150 cubic meters per day
Php 24,000 More than 150 cubic meters per day

The fixed fee also depends on the volume of wastewater discharged. Table 4 summarizes the fixed fees depending on the volume of wastewater discharge and the presence of heavy metals. For a firm that discharges wastewater without heavy metals, the fee would be 24,000 pesos if the discharge is more than 150 cubic meters per day, 16,000 pesos if the discharge is between 30 to 150 cubic meters per day and 8,000 pesos if the discharge volume is less than 30 cubic meters per day. Those firms that discharge wastewater with heavy metals, on the other hand, pay higher fixed fees. The fee would be 12,000 pesos for a firm that discharge less than 150 cubic meters of wastewater with heavy metals per day and 24,000 if the discharge is more than 150 cubic meters per day.

The variable fee, on the other hand, is calculated with the reference to the BOD5 loading as well as to the volume and concentration of the wastewater being discharged. According to the same policy, the variable fees is 30 pesos per kilogram of total BOD5 when the BOD concentration is less than 50 milligrams per liter and 30 pesos per kilogram of total BOD5 when the BOD5 concentration is greater that 50 milligrams per liter.

External links

References

Amsberg, J. V. (1995) Selected experiences with the use of economic instruments for pollution control in non-OECD countries. Journal retrieved from http://www.vonamsberg.net/joachim/econw.htm

Asian Development Bank (1997). Potential uses of market-based instruments for environmental management in the Philippines - the essentials. Unpublished manuscripts from Asian Development Bank's Office of Environment and Social Development. Mandaluyong City.

Barde, J. (2000). Implementing environmental taxes in OECD countries. Journal retrieved from http://www.env.cz/www/zamest.nsf/defc72941c22 3d62c12564b30064fdcc/b1a19694e78d6a24c12568fc004b734d? OpenDocument. August 30, 2005.

Barde, J.& Smith, S. (1997), Do economic instruments help the environment? The OECD Observer, No. 204

Baumol, W. & Oates, W. (1988) The theory of environmental policy. Cambridge University Press

Batu, M. (1996) Factors affecting productivity of selected inland bodies of water in the Philippines: The case of the Laguna Lake 1986 to 1996. Undergraduate thesis. San Beda College, Manila.

Becker, G. S. (1968). Crime and punishment: An economic approach. Journal of Political Economy. 76, 169 - 217

Bluffstone, R. A. (2002) Environmental taxes in developing and transition economies. Journal retrieved from www.econ.pdx.edu/staff/rb/taxes.pdf

Canonoy, F. V. (1997). Lake Laguna's environmental user fee system. Journal retrieved from http://www.unescap.org/drpad/vc/conference/bg_ph_14_lle.htm August 12, 2005

Congress of the Republic of the Philippines (2002). Clean Water Act of 2002: Author

Cohen, M. (1998) Monitoring and enforcement of environmental policy. Journal retrieved from http://www.law.duke.edu/journals/delpf/articles/DELPF10P221.HTM#B5 August 15, 2005.

Coase, R. (1960). The problem of social cost. Journal of Law and Economics 3, 1-44

Dasgupta, S., Huq, M. & Wheeler, D. (1997) Bending the Rules: Discretionary Pollution Control in China Journal retrieved from http://www.worldbank.org/nipr/ work_paper/1761/

Danao, R. (2002) Introduction to economic statistics and econometrics. University of the Philippines Press. Diliman, Quezon City, Philippines

Davies, E. (1986). Laguna de bay problems & options. Unpublished research material from LLDA. Pasig, Philippines.

Department of Environment and Natural Resources Administrative Order 35 series of 1990, as amended. Retrieved from http://www.denr.gov.ph/policy/1990/ENV_DAO_1990-35.pdf

Department of Environment and Natural Resources. Clean Water Act of 2002 Implementing Rules and Regulations. Retrieved from http://www.denr.gov.ph/policy/2005/dao/dao2005-10.pdf

Downing, P. & Watson, W. (1974) The economics of enforcing air pollution controls. Journal of Environmental Economics and Management 219 – 236

Environmental Protection Agency (2004) International experiences with economic incentives for protecting the environment. Journal retrieved from http://www.iisd.org/susprod/search.asp January 15, 2006

Eskeland, G. & Jimenez, E. (1992) Policy instruments for pollution control in developing countries. The World Bank Research Observer 7 145 – 169

Gonzales, E. (1987) A socio economics geography (1961 – 85) of the Laguna lake resources and its implications to aquatic resources management and development of the Philippine islands. Dissertation. Cambridge University, England, United Kingdom

Guerrero, R. & Calpe, A. T. (1998) Water resources management : A global priority. National Academy of Science and Technology, Manila, Philippines

Hagler Bailly Consulting Inc. (1996) An action program for the introduction of economic incentives to promote water pollution prevention and abatement in the Philippines: Final report. Published by Hagler Bailly Consulting Inc. for the LLDA. Arlington Virginia USA

Harford, J. (1998) Firm behavior under imperfectly enforceable pollution standards and taxes. Journal of Environmental Economics and Management 26 – 43

Hayes, A. G. (1994) Discharge taxes when regulatory jurisdiction is incomplete. Scottish Journal of Political Economy 41 278 - 285

Huang, C. (1996) Effectiveness of environmental regulations under imperfect enforcement and firms avoidance behavior. Environment and Resource Economics 8, 183-184

Jones, C. A. (1984) Standard setting with incomplete enforcement revisited. Journal of Policy Analysis and Management 8, 72 – 87

Laguna Lake Development Authority (2004). The Environmental User Fee System. Pasig City, Metro Manila: Author.

Laguna Lake Development Authority (2005) Laguna de Bay environment monitor: A report to the stakeholders of the Laguna de Bay Region. Pasig City, Metro Manila: Author

Laguna Lake Development Authority (1996) Annual financial report CY 1996. Pasig City, Metro Manila: Author

Laguna Lake Development Authority (1997) Annual financial report CY 1997. . Pasig City, Metro Manila: Author

Laguna Lake Development Authority (1998) Annual financial report CY 1998. Pasig City, Metro Manila: Author

Laguna Lake Development Authority (1999) Annual financial report CY 1999. . Pasig City, Metro Manila: Author

Laguna Lake Development Authority (2000) Annual financial report CY 2000. . Pasig City, Metro Manila: Author

Laguna Lake Development Authority (2001) Annual financial report CY 2001. . Pasig City, Metro Manila: Author

Laguna Lake Development Authority (2002) Annual financial report CY 2002. . Pasig City, Metro Manila: Author

Laguna Lake Development Authority (2003) Annual financial report CY 2003. . Pasig City, Metro Manila: Author

Laguna Lake Development Authority (2004) Annual financial report CY 2004. . Pasig City, Metro Manila: Author

Laguna Lake Development Authority (1986)Water quality report on the Laguna de Bay and its tributary rivers. Pasig City, Metro Manila: Author

Laguna Lake Development Authority (1987) Water quality report on the Laguna de Bay and its tributary rivers. Pasig City, Metro Manila: Author

Laguna Lake Development Authority (1988) Water quality report on the Laguna de Bay and its tributary rivers. Pasig City, Metro Manila: Author

Laguna Lake Development Authority (1996) Water quality report on the Laguna de Bay and its tributary rivers. Pasig City, Metro Manila: Author

Laguna Lake Development Authority (1997)Water quality report on the Laguna de Bay and its tributary rivers. Pasig City, Metro Manila: Author

Laguna Lake Development Authority (1998) Water quality report on the Laguna de Bay and its tributary rivers. Pasig City, Metro Manila: Author

Laguna Lake Development Authority (1999)Water quality report on the Laguna de Bay and its tributary rivers. Pasig City, Metro Manila: Author

Lanna, E (1995) Water charges in Brazil: Implementation and perspectives. Journal retrieved from www.iadb.org/SDS/doc/Water_Pricing_and_Pub-Pri_Partnership-6.pdf

Lee, D. (1984) The economics of enforcing pollution taxation. Journal of Environmental Economics and Management 11, 147-160

Malik, A. S. (1992) Enforcement costs and the choice of policy instruments for controlling pollution. Economic Inquiry 714 – 721

McKitrick, R. (1999) A derivation of the marginal abatement cost curve. Journal retrieved from http://www.uoguelph.ca/~rmckitri/teaching/mac.doc January 30, 2006

National Statistical Coordination Board (1996) Estimation of fish biomass in Laguna de Bay based on primary productivity. Article retrieved from www.nscb.gov.ph/peenra/Publications/biomass/lagunalake-text.pdf January 18, 2006.

Nepomuceno, D. (2004), The environmental user fee system in the Laguna de Bay Region: A pioneer market-based Instrument for pollution prevention and abatement in the Philippines. Retrieved from http://www.adb.org/Water /Seminars/2004/pdf/blue-bag-16-full-paper-LLDA.pdf#search='environmental %20user%20fee%20system'

Nicholson W. (2002) Microeconomics: Principles and extensions. Prentice Hall. USA

OECD (1993). The Experiences of Brazil, Mexico, Chile, and Argentina in the use of economic instruments in environmental policy. Informal Workshop on the Use of Economic Instruments in Environmental Policies. Retrieved from http://www.oecd.org/topic/0,2686,en_2649_33991_1_1_1_1_37465,00.html

Oh, Y. (1993) Surveillance or punishment? A secondbest theory of pollution regulation. International Economics Journal 9 (3)

Solidarity for People’s Power (1992) Laguna de bay: Racing against time. Pamphlet article. Los Baños, Laguna, Philippines.

Taylor, C, Yahner J., & Jones, D. Wastewater. Article retrieved from http://danpatch.ecn.purdue.edu/~epados/septics/wwater.htm

United Nations (1998) Economic instruments: Report on the use of economic instruments for environmental policy in Central and Eastern Europe. Background document retrieved from http://www.mem.dk/aarhus-conference/issues/htm

University of the Philippines Los Baños (2005) Ecosystems and people: The Philippine millennium ecosystem assessment (MA) sub global assessment. Los Baños, Laguna: Author

Varian, H. (2000) Microeconomics Prentice Hall

Vincent, J (1997) Reducing effluent while raising affluence: Water pollution abatement in Malaysia. Harvard Institute for Development.

Viscusi, W. & Zeckhauser, R. (1979) Optimal standards with incomplete enforcement. Public Policy 27, 437 – 456

World Bank (1992) China: Environmental strategy. Article retrieved from Paperhttp://web.worldbank.org/WBSITE/EXTERNAL/COUNTRIES/EASTASIAPACIFICEXT/EXT January 20, 2006

 


From Wikipedia, the Free Encyclopedia. Original article here. Support Wikipedia by contributing or donating.
All text is available under the terms of the GNU Free Documentation License See Wikipedia Copyrights for details.

Search Titles
0123456789
ABCDEFGHIJ
KLMNOPQRST
UVWXYZ?

E-mail this article to:

Personal Message: