MONITORRING OF ORGANIC POLLUTANTS IN STREAMS AND A RESERVOIR
(case study in
Selorejo Dam, Malang ,Jawa Timur, Indonesia)
BAMBANG PARI PURWANTO
Brawijaya
University, Malang, East of Java, Indonesia
Jl. Mayjen Haryono No.167, Telp.
0341-553286, 587710, 587711, Fax. 0341-551430 Malang 65145
Email : goparipung@yahoo.com
ABSTRACT
The Efect of fertilizer in land
agriculture has become decreasing water quality that couse Eutrophication. Analysis Method that used is analysis
model with AVSWAT 2000, at characteristic of study area are : 237.312 km2
catchment area of Selorejo Dam, simulation devide in 62 subwatershed area
cacthment, including : Forest 0.395 %, mix-dry field 0.128 %, Rice Field 0.214
%, dry land 0.154 %, Urban 0.088 %, lake 0.021 %. The result show that the power river
concerning to load polutant is calss III,that value is minimaly for categoried
on good water quality . The result of simulation model 2003-2005 has become
decreasing lake water quality, 18.5 % dan 23.5 %, total N (Mesotrophic)and Total
P (Eutrophic). Meanwhile, the alteration of landuse in 2010 latters couses
increasing load pollutant in lake of Selorejo DAM. The deviation of Model
AVSWAT 2000, concerning to discarge model and measurement, R2 value is 0.9303, significance level ≤10, concerning to
load polutant, R2 value is 0.907, significance level ≤10. The result of models
are nonhomogeneous form time by time but homogeneous form space model and
measurement.
Keywords :
power river, Mesotrophic, Eutrophic
INTRODUCTION
In lake of selorejo,
identifacated that load pollutan condition has increased, that proofed by
measurement record :
Figure.4 Measurement Record of NO3 in Lake Of Selorejo
So that condition needs control and
monitorring as early as possible.
PURPOSE OF STUDY
The aim of the
study is to give a information about value and patern of pollutan distribution
because of crop management in location study, as a particularly reference
concerning risk monitoring water quality in lake of selorejo and for instrument
test a correctness of the AVSWAT 2000 Model (Soil and Water Assessment Tool
2000).
Purpose Of The Study : Predicate of risk level Eutrophication couse agriculture
pollutant from N and P element..
THE
STUDY AREA
A. Location
The Brantas River basin is located in east Java
province on the island
of Java, Indonesia and
lies between 1100 300 and 1120 550
east longitude and 70 010
and 80 150 south latitude. The Brantas River
originates on the slopes of Mt Arjuno (3400 msl), and follows a clockwise
direction through Malang
and Kediri, and
branching into two distributaries at Mlirip, the Surabaya and Porong river. It has a watershed
area of about 11,800 km2, stretches 320 km. The six sub basin are Lesti Basin
(625 km2), Konto
Basin (687 km2),
Widas Basin (1,539 km2), Brantas Basin (6,719 km2), Ngorowo
basin (1600 km2) and Surabaya
basin (631 km2),
The study area is
Selorejo Reservoir that located at upper of Konto River.
It has a Catchment area of 235 km2 at dam site of Selorejo
Reservoir, and maximum reservoir capacity is 62.30 million m3, with
an effective reservoir capacity of 50.10 million m3.
B. Land Use and Soil Type
Stream water
quality monitoring can be used to determine the impacts from different land
uses in watershed to the overall water quality. In watershed with mixed land
uses (forest, agricultural and urban), stream commonly show elevated nutrient
concentration (Spahr and Wynn, 1997). Typically one of the highest sources of
nutrient in the Selorejo watershed are the agricultural areas, this is due to
the application of fertilizer/pesticides and disturbance of soil for
agricultural production purpose.
The land use
categories in the Selorejo
River Basin were
development using satellite imager.
Land use
information was collected using Global Positioning System (GPS) equipment and
transferred to GIS using Arc View software (ESRI. 2004). Five land use type
were considered: urban area, dry field, rice field, mixed-dry field and Forest
Table
4. Distribution of Soil Type in Selorejo Catchment area
Soil Type
|
Area (km2)
|
% Total
|
16.41
|
6.976
|
|
Grumosol
|
164.31
|
69.869
|
Mediteran
|
27.03
|
11.492
|
Andosol
|
27.42
|
11.662
|
Total (km2)
|
235.17
|
100%
|
Water quality
monitoring for nutrient requires accurate of stream surface water velocity. For
this reason the sampling method, frequency and analysis are some of the
principal factor to consider for constituent loads determination. Due to the
negative impacts that excess of nutrient can cause to water bodies
(eutrophication) it is important to determinate concentration, trends and loads
of these pollutants and associates then to possible contributors (NPS or PS).
To exactly determinate of Nutrient load is difficulty. Several methods can be
applied for this purpose like, interpolation, regression and average
techniques.
The primary water
pollutant load in study area was two categories, first from Agriculture area
and second from urban area. According
from Department of Agriculture Malang-East Java data, commonly farmers in study
area using fertilizing with Urea (Ca(NH2)2); TSP (Ca(H2PO4)2);
KCL and ZA. (see Table 5). Farmers on the site study use much fertilizer and
pesticides more than normal regulation. Wastewater from urban area was
calculated which assumed that human faces contain 14,5 g.N/day/person;1,9
g.P/day/person and Urine contain 7 g. N/day/person, 2 g.P/day/person. (Dyah,
R., 2002,. 11-12)
Table
5. Using fertilizer for each plant.
Plant
|
Fertilizer (kg/ha)
|
|||
Urea
|
TSP
|
KCL
|
ZA
|
|
Rice
|
250-300
|
50-100
|
50-75
|
100
|
Corn
|
200
|
100
|
50
|
100
|
Soybean
|
50
|
50
|
50
|
50
|
RESULTS
AND DISCUSSION
Result of SWAT
simulation was divided into tree phases, first in land area, second in stream
and finally at reservoir.
RESERVOIR
PHASE SIMULATION
Conclusion
The SWAT model was
the first time applied to the Selorejo reservoir Catchment area which is
located in Brantas
River basin East Java. The model was calibrated for the flow and
initial results are presented for the nitrogen and phosphorous loadings in the
watershed.
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