Syntax Literate: Jurnal Ilmiah Indonesia p–ISSN: 2541-0849 e-ISSN: 2548-1398
Vol. 9, No. 12, Desember 2024
ANALYSIS OF
PLANNED FLOOD DISCHARGE IN THE GROMPOL WATERSHED
Aprilia Indah Wulandari1, Erni Mulyandari2, Teguh Yuono3
Universitas Tunas Pembangunan,
Indonesia1,2,3
Email: [email protected]1, [email protected]2, [email protected]3
Abstract
The Grompol watershed is one of the sub-watersheds of Bengawan Solo located in Karanganyar
Regency and Sragen Regency. When the intensity of
rainfall is high, the area downstream of the Grompol
River often floods to cause many losses. Therefore, analyzing the planned flood
discharge as a reference in flood control efforts is necessary. This study aims
to identify the most common problems in the Grompol
River flow, identify flood points in the Grompol
River and its countermeasures, analyze the size of the Grompol
Watershed using QGIS
3.10.6 Software, and calculate the amount of planned flood discharge in the Grompol Watershed. The method in this study is the Nakayasu Synthesis Unit Hydrograph Method, with a repeat
period of 25 years. The analysis stage begins with conducting a location survey
and interviews and then conducting a planned flood discharge analysis. Based on
the results of the research, it was found that the problems that occur a lot in
the Grompol River flow are sediment, organic waste,
and inorganic waste, as well as streams that have been flooded at 4 points out
of 31 survey locations, namely in the settlements around the Gedangan Lor Bridge, Gading Grompol,
Gantung Kedusan, and Pringanom, where flood control efforts are dominated in the
form of community service, an area of the Grompol
watershed is obtained using Software QGIS 3.10.6 is 164,95 km2 while
for flood discharge for the 25-year recurrence period using the Nakayasu Synthetic Unit Hydrograph Method of 623,32 m3/s.
Keywords: QGIS, Grompol
Watershed, Planned Flood Discharge, Nakayasu Method.
Introduction
The Grompol
River is one of the tributaries of the Bengawan Solo
River, which flows in two districts, namely Karanganyar
Regency and Sragen Regency, where the upstream is on
Mount Lawu and downstream in Masaran
District, Sragen Regency. When rainfall intensifies,
the area downstream of the Grompol River, precisely
in Sragen Regency, often experiences flooding.
The flood problem once occurred in Sragen Regency at the end of 2022; the flood occurred due
to high rainfall, so the Grompol River overflowed.
The overflow of the Grompol River has caused several
hamlets in Sidodadi Village, Masaran
District, and Sragen Regency to be flooded. The
hamlets that experienced the flood include Nogosari
Hamlet, Driyan Hamlet, and Grompol
Hamlet, which have water levels of 30 cm. In addition, the Bayur
Bridge in Kliwonan Village, Masaran
District, also collapsed due to the flood. The rapid flow of the Grompol River carries large clumps of bamboo materials, and
then the material hits the bridge pillars, causing the pillars to break and the
bridge to collapse.
Based on the problems described above, it is
necessary to calculate and analyze planned flood discharge for flood management
and water infrastructure planning. Therefore, a study was conducted titled
"Analysis of Planned Flood Discharge in the Grompol
Watershed."
Research related to flood discharge analysis has been carried out a
lot, including research on the analysis of the flood hydrographic model of the Ngotok River using the SCS, Snyder, and Nakayasu
Methods. The results of the flood hydrograph calibration with a 25-year reage calculated using the Nash formula obtained a value of
0,88 for the SCS Method, 0,74 for the Snyder Method, and 0,43 for the Nakayasu Method. Based on these results, the value of the
SCS hydrograph is close to the value of the field hydrograph
Flood discharge analysis
was also conducted in the Buntung River in Sidoarjo Regency using the Nakayasu
Method. Based on the results of the calculation using this method, it was
obtained that the amount of flood discharge of the Buntung
River with a 25-year recurrence period of 196,923 m3/s
Comparison of estimated
peak flood discharge using the Nakayasu and the
Javanese Sumatra FSR methods in the Dombo Sayung watershed. Based on the results of the analysis, the
flood discharge value using the Nakayasu Method for
the Penggaron River was 270,4 m3/s, the Dombo Sayung River was 296,4 m3/s,
and the Dolok River was 332,2 m3/s.
Meanwhile, with the Javanese Sumatra FSR Method, the flood discharge value for
the Penggaron River was 112,7 m3/s, the Dombo Sayung River was 239,7 m3/s,
and the Dolok River was 632,1 m3/s
Analysis of the flood
discharge of the Palu River plan using the Nakayasu
synthetic unit hydrograph. Based on the results of the study, it was found that
the magnitude of flood discharge in the 2, 5, 10, 25 and 50-year re-periods was
Q2 year = 966,372 m3/s, Q5 year
= 1131,194 m3/s, Q10 year = 1235,828 m3/s, Q25
year = 1364,332 m3/s, dan Q50 year = 1458,269 m3/s
Flood discharge analysis
of the Uru Ino River, East
Halmahera Regency, using the hydrographic approach of Gama I and Nakayasu synthetic units. Based on the results of the
analysis, it was obtained that the amount of flood discharge using the Gama 1
Method with a 2-year recurrence period of 64,916 m3/s, 5-year reage of 131,619 m3/s, 10-year reage of 159,727 m3/s, 25-year reage of 183,485 m3/s, and the 50-year money
period is 195,440 m3/s. Meanwhile, the Nakayasu
Method obtained a 2-year re-annual discharge of 124,15 m3/s, 5-year reage of 157,91 m3/s, 10-year reage of 172,15 m3/s, 25-year reage of 184,19 m3/s, and the 50-year reage of 190,25 m3/s
Analysis of the design
flood discharge in the Tulang Bawang River, Lampung
Province, using the Nakayasu Method. Based on the
results of the study, it was found that the amount of flood discharge at the
2-year reage was 427.10 m3/s, the 5-year re-era was
631,29 m3/s, the 10-year reage is 797,07 m3/s,
20-year reage is 999,64 m3/s, 25-year reage is 1045,96 m3/s, 50-year reage of 1262,56 m3/s, and the 100-year reage of 1508,82 m3/s
The design flood discharge analysis was conducted in the Tukad Mati Watershed using the Nakayasu,
Snyder, and Rational Method. The results of the Nakayasu
Method show a 10-year recurrent discharge value of 223,195 m3/s and
a 25-year reage of 243,370 m3/s. The
results of the Rational Method show that the discharge of the 10-year reage is 147,880 m3/s, the 25-year reage is 16,248 m3/s, while the results of the
Snyder Method showed a 10-year reage discharge of
137,651 m3/s, a 25-year reage of 150,095 m3/s,
so it can be said that the results of the Snyder Method show the lowest flood
discharge value
Planned flood discharge analysis using the Nakayasu
Synthetic Unit Hydrograph Method in the Cimandiri
River Basin. Based on the results of the study, it was obtained that the
planned flood discharge for the 2-year recurrence period was 2654,4 m3/s,
the 5-year recurrence period was 3815,3 m3/s, the 10-year recurrence
period was 4534,3 m3/s, the 50-year recurrence period was 6133,9 m3/s,
and the 100-year recurrence period was 6833,2 m3/s
Analysis of design flood discharge in
the Selabung watershed using the Nakayasu synthetic unit hydrograph method.
Based on the calculation results, the amount of flood discharge of the Serabung
watershed plan with a 100-year recurrence period of 36,89 m3/s
Flood analysis of the hydrographic method of SCS synthetic units and
Nakayasu watershed Pesung, Batam. The calculation results show that the most
significant flood discharge occurred in the SCS-CN Method with a flood
discharge of 215,488 – 584,308 m3/s for the 5-year recurrence
period, while in the Nakayasu Method, it was 360,526
– 986,535 m³/s
Based on the literature study in the journal mentioned above, it is known that the analysis of flood discharge in the Grompol watershed has never been carried out. The difference between this study and previous research lies in the research location, rainfall data, and the rain station used.
The purpose of this study is to identify the most common problems in the Grompol River flow, identify flood points in the Grompol River and its countermeasure efforts, analyze the size of the Grompol Watershed using QGIS 3.10.6 Software, and calculate the amount of planned flood discharge in the Grompol Watershed.
Research Methods
This research stage
begins by identifying the problems in the Grompol
watershed, and then the background and formulation of the research problem are
drawn; a preliminary study is also carried out. The location of the Grompol watershed can be seen in Figure 1.
Figure 1. Research Location in the Grompol Watershed
(Source: Google Earth, 2024)
Furthermore, data
collection was carried out using primary and secondary data. Surveys and
interviews obtained primary data, while secondary data was obtained from
related agencies and online data sites, including watershed maps, rainfall
data, National Digital Elevation Model data, Indonesian Terrain Map, and HSGs
Map.
The data analysis was
divided into four stages, namely identifying problems that occur in the Grompol River flow from the results of the flow survey,
identifying flood points in the Grompol River flow
and countermeasures from the results of interviews, analyzing the area of the Grompol watershed using
QGIS 3.10.6 Software from the National Digital Elevation Model data, and
calculating the planned flood discharge from 4 data, namely rainfall data that
had previously been tested for consistency,
watershed area, Indonesian Terrain map to find land use, and HSGs map to
find soil class. The final stage is drawing conclusions and suggestions from
the discussion results at the data analysis stage.
Results and Discussion
Identification of Grompol River Flow Problems
The survey points taken
are at bridge points and surrounding settlements along the Grompol
River flow from upstream to downstream, with the number of survey points being
31. The Grompol River flow survey uses three
parameters in its observations: sediment, waste (organic and inorganic waste),
and wild plants on the river embankment. The Grompol
River flow survey was completed within three days, from Monday, April 29, 2024,
to Wednesday, May 01, 2024. The results of the river flow survey activities are
presented in the form of a network scheme, which can be seen in Figure 2, while
a recapitulation of river flow conditions can be seen in Figure 3.
Figure
2. Network Schematic
(Source: Personal Documentation, 2024)
Figure
3. Recapitulation of Grompol River Flow Condition
Data
(Source: Personal Calculations, 2024)
Based on Figure 3, it
can be concluded that of the 31 survey points, 74% of the flow points contained
sediment, 97% contained organic waste, 61% contained inorganic waste, and 39%
contained wild plants in the river infrastructure.
Identification of Flood Points of the Grompol
River Flow and Countermeasures
Interviews with
residents around the bridge points can help identify flood points. The number
of respondents from the interview was 31, and the bridge point reviewed them.
The results of the interview recapitulation can be seen in Figure 4.
Figure
4. Recapitulation of Interview Data
(Source: Personal Calculations, 2024)
Based on Figure 4, it
can be concluded that 13% of 31 respondents said that there had been overflows
that caused flooding at 4 points, namely in settlements around the Gedangan Lor Bridge, Gading Grompol
Bridge, Gantung Kedusan
Bridge, and Pringanom Bridge, where flood management
efforts from the government and local communities were dominated in the form of
community service.
Grompol Watershed Area Analysis Using QGIS 3.10.6 Software
The extensive analysis
of the Grompol watershed was carried out using QGIS 3.10.6
Software, namely by entering the National Digital Elevation Model data obtained
from the official website of the Indonesian homeland. The results of the Grompol watershed in QGIS 3.10.6 Software can be seen in
Figure 5.
Figure
5. Results of Grompol Watershed Area
(Source: QGIS 3.10.6, 2024)
Based on Figure 5, it
can be seen
that the area of the Grompol
watershed using QGIS 3.10.6 Software
is 164,95 km2.
Calculation of Flood Discharge of the Grompol
Watershed Plan
According to
1) Rain Data Consistency Test
Rainfall data was taken from rainfall
stations closest to the Grompol watershed, including
the Tawangmangu Rainfall Post in 2004 - 2023, Delingan Rainfall Post in 2012 - 2023, and Karangpandan Rainfall Post in 2014 - 2023. The
recapitulation of total annual rainfall from the three stations can be seen in
Table 1.
Table 1 Recapitulation of Total Annual
Rainfall
Year |
Total
Rainfall (mm) |
||
Tawangmangu
Station |
Delingan Station |
Karangpandan Station |
|
2004 |
2960 |
- |
- |
2005 |
3387 |
- |
- |
2006 |
2542 |
- |
- |
2007 |
2970 |
- |
- |
2008 |
2240 |
- |
- |
2009 |
3106 |
- |
- |
2010 |
4682 |
- |
- |
2011 |
3334 |
- |
- |
2012 |
2217 |
1864 |
- |
2013 |
2770 |
2268 |
- |
2014 |
2571 |
1244 |
2510 |
2015 |
3171 |
2218 |
3097 |
2016 |
4759 |
3717 |
5006 |
2019 |
2889 |
1842 |
2526 |
2020 |
4157 |
2231 |
3210 |
2021 |
4084 |
2820 |
3148 |
2022 |
4154 |
3060 |
4129 |
2023 |
2394 |
1743 |
1812 |
(Source: Bengawan Solo River Region
Headquarters, 2024)
According to
Table 2. Consistency Test
Results
Rain
Station |
Consistency
Test Requirements |
Information |
|
Tawangmangu |
1. |
Qcount
< Qcritics |
Consistent |
4.03 < 5.46 |
|||
2. |
Rcount
< Rcritics |
||
5.15 < 6.40 |
|||
Delingan |
1. |
Qcount
< Qcritics |
Consistent |
2.19 < 4.00 |
|||
2. |
Rcount
< Rcritics |
||
2.99 < 4.54 |
|||
Karangpandan |
1. |
Qcount
< Qcritics |
Consistent |
1,68 < 3,60 |
|||
2. |
Rcount
< Rcritics |
||
2,29 < 4,05 |
(Source: Personal Calculations, 2024)
Based on Table 2, the data
from Tawangmangu Station, Delingan
Station, and Karangpandan Station are consistent.
2) Determination of
Regional Rainfall
According to
Table 3. Maximum Rainfall Recapitulation
k |
Year |
P max |
1 |
2004 |
127,00 |
2 |
2005 |
171,00 |
3 |
2006 |
89,00 |
4 |
2007 |
194,00 |
5 |
2008 |
107,00 |
6 |
2009 |
121,00 |
7 |
2010 |
128,00 |
8 |
2011 |
116,00 |
9 |
2012 |
100,50 |
10 |
2013 |
65,50 |
11 |
2014 |
58,00 |
12 |
2015 |
82,67 |
13 |
2016 |
106,33 |
14 |
2017 |
95,33 |
15 |
2018 |
102,33 |
16 |
2019 |
108,33 |
17 |
2020 |
108,00 |
18 |
2021 |
111,33 |
19 |
2022 |
100,67 |
20 |
2023 |
90,33 |
(Source: Personal Calculations, 2024)
3) Distribution Fit Test
According to
a) Parameters Statistics
The results of the Distribution Fit Test
with Statistical Parameters can be seen in Table 4.
Table 4. Statistical Parameter Distribution Match Test
No |
Distribution |
Requirement |
Condition |
Calculation Results |
Information |
1 |
Normal |
(X average ± s) = 68,27% |
68,27% |
80,00% |
Rejected |
(X average ± 2s) = 95,44% |
95,44% |
95,00% |
Rejected |
||
Cs ≈ 0 |
0 |
1,19 |
Rejected |
||
Ck ≈ 3 |
3 |
5,81 |
Rejected |
||
2 |
Log-Normal |
Cs = Cv3+3Cv |
1,19 |
0,88 |
Rejected |
Ck = Cv8+6Cv6+15Cv4+ 16Cv2+3 |
5,81 |
4,39 |
Rejected |
||
3 |
Gumbel |
Cs = 1,14 |
1,14 |
1,19 |
Rejected |
Ck = 5,4 |
5,4 |
5,81 |
Rejected |
||
4 |
Log Pearson Type III |
Others |
Others |
Accepted |
|
Possible distribution: |
Log Pearson Type III |
(Source: Personal Calculations, 2024)
Based on Table 4, the statistical parameter
requirements for the Normal, Log Normal, and Gumbel distributions are not met,
so it is estimated that the appropriate distribution type is the Log Pearson
Type III distribution.
b) Smirnov Klomogorov
By
Table 5. Smirnov Kolmogorov
Distribution Compatibility Test
No |
Distribution
Type |
Smirnov
Kolmogorov Test Requirements |
|||
∆
max |
< |
∆
critics |
Conclusion |
||
1 |
Normal Distribution |
0,14 |
< |
0,29 |
Accepted |
2 |
Normal Log Distribution |
0,10 |
< |
0,29 |
Accepted |
3 |
Gumbel Distribution |
0,12 |
< |
0,29 |
Accepted |
4 |
Distribusi
Log Pearson Type III |
0,10 |
< |
0,29 |
Accepted |
(Source: Personal Calculations, 2024)
Based on Table 5, it can be said that the
Smirnov Kolmogorov test for all types of distributions is accepted with the
smallest ∆max value, namely the Gumbel and Log Pearson Type III distributions.
c) Chi-Squared
According to
Table 6. Chi-Squared Distribution Fit
Test
No |
Distribution
Type |
Requirements
for Quadratic Chi Test |
|||
|
< |
|
Conclusion |
||
1 |
Normal Distribution |
4,00 |
< |
5,99 |
Accepted |
2 |
Normal Log Distribution |
5,50 |
< |
5,99 |
Accepted |
3 |
Gumbel Distribution |
5,50 |
< |
5,99 |
Accepted |
4 |
Distribusi
Log Pearson Type III |
5,50 |
< |
5,99 |
Accepted |
(Source: Personal Calculations, 2024)
Based on Table 6, the Chi-Square Test for
all types of distributions is accepted with the smallest chi-squared value,
namely the normal distribution.
The recapitulation of the distribution
match test of the three methods can be seen in Table 7.
Table 7. Recapitulation of
Distribution Fit Test
No |
Distribution
Type |
Distribution
Fit Test |
||
Parameters
Statistics |
Smirnov
Kolmogorov |
Chi
Kuadrat |
||
1 |
Normal Distribution |
Rejected |
Accepted |
Accepted |
2 |
Normal Log Distribution |
Rejected |
Accepted |
Accepted |
3 |
Gumbel Distribution |
Rejected |
Accepted |
Accepted |
4 |
Distribusi
Log Pearson Type III |
Accepted |
Accepted |
Accepted |
(Source: Personal Calculations, 2024)
Based on Table 7, the
distribution type of Log Pearson Type III was taken for the following
calculation because the distribution was accepted in the three distribution
match tests.
d) Rainfall Distribution
The type of rainfall
distribution used is Pearson Log Distribution Type III with a re-period of 25
years. The calculation of rainfall Log Pearson Type III can be seen in Table 8.
Table 8. Calculation of Pearson
Type III Log
k |
Year |
Pmax |
ln
Pmax |
(ln
Pmax - ln Prerata) |
(ln
Pmax - ln Prerata)2 |
(ln
Pmax - ln Prerata)3 |
1 |
2004 |
127,00 |
4,84 |
0,19 |
0,04 |
0,01 |
2 |
2005 |
171,00 |
5,14 |
0,49 |
0,24 |
0,11 |
3 |
2006 |
89,00 |
4,49 |
-0,17 |
0,03 |
0,00 |
4 |
2007 |
194,00 |
5,27 |
0,61 |
0,37 |
0,23 |
5 |
2008 |
107,00 |
4,67 |
0,02 |
0,00 |
0,00 |
6 |
2009 |
121,00 |
4,80 |
0,14 |
0,02 |
0,00 |
7 |
2010 |
128,00 |
4,85 |
0,20 |
0,04 |
0,01 |
8 |
2011 |
116,00 |
4,75 |
0,10 |
0,01 |
0,00 |
9 |
2012 |
100,50 |
4,61 |
-0,05 |
0,00 |
0,00 |
10 |
2013 |
65,50 |
4,18 |
-0,47 |
0,23 |
-0,11 |
11 |
2014 |
58,00 |
4,06 |
-0,60 |
0,36 |
-0,21 |
12 |
2015 |
82,67 |
4,41 |
-0,24 |
0,06 |
-0,01 |
13 |
2016 |
106,33 |
4,67 |
0,01 |
0,00 |
0,00 |
14 |
2017 |
95,33 |
4,56 |
-0,10 |
0,01 |
0,00 |
15 |
2018 |
102,33 |
4,63 |
-0,03 |
0,00 |
0,00 |
16 |
2019 |
108,33 |
4,69 |
0,03 |
0,00 |
0,00 |
17 |
2020 |
108,00 |
4,68 |
0,03 |
0,00 |
0,00 |
18 |
2021 |
111,33 |
4,71 |
0,06 |
0,00 |
0,00 |
19 |
2022 |
100,67 |
4,61 |
-0,04 |
0,00 |
0,00 |
20 |
2023 |
90,33 |
4,50 |
-0,15 |
0,02 |
0,00 |
Sum |
2182,33 |
93,13 |
0,00 |
1,42 |
0,02 |
(Source: Personal Calculations, 2024)
Standard deviation (Sd) = = = 0,27
Coefficient of skewness (Cs) =
= 0,05
The KT value is obtained from the KT table
of the Pearson III Log Distribution, where for a value of Cs = 0.05 with a
return period of 25 years, the KT value = 1.769 is obtained.
= 5,140
X25 years = exp (5,140)
X25 years = 170,775 mm ≈ 170,77 mm
So, from the Pearson Type III Log Distribution calculation, the 25-year planned rainfall was obtained at 170,77 mm.
e) Rain Hyetograph Design
Daily
rainfall data is changed by changing the depth of hourly rainfall using a
rainfall distribution model Alternating Block Method (ABM). According
to
Table 9 .
Draft Rain Hyetograph (ABM)
Td |
Δt |
It |
It
Td |
Δp |
Pt |
hyetograph |
|
(jam) |
(jam) |
(mm/him) |
(mm) |
(mm) |
(%) |
(%) |
(mm) |
[1] |
[2] |
[3] |
[4] |
[5] |
[6] |
[7] |
[8] |
1 |
0~1 |
59,20 |
59,20 |
59,20 |
63,00 |
11,49 |
19,62 |
2 |
1~2 |
37,30 |
74,59 |
15,39 |
16,37 |
63,00 |
107,58 |
3 |
2~3 |
28,46 |
85,39 |
10,79 |
11,49 |
16,37 |
27,96 |
4 |
3~4 |
23,50 |
93,98 |
8,59 |
9,14 |
9,14 |
15,62 |
Sum |
93,98 |
100 |
100 |
170,77 |
(Source: Personal Calculations, 2024)
Based on Table 9, the rain hyetograph value with the
ABM method for the first hour is 19,62 mm, the second hour is 107,58 mm, the
third hour is 27,96 mm, and the fourth hour is 15,62 mm, where the rain value
is then used for the calculation of adequate rain.
f) Effective Rain
The stage of calculating adequate rain begins with
calculating the composite CN value, which is then used in the basic equation to
determine the amount of proper rainfall. The data needed to determine the
composite CN value are land use data and soil type. The land use map and soil
type map of the Grompol watershed using QGIS 3.10.6 Software can be seen in
Figure 6 and Figure 7.
Figure 6. Land Use Map of Grompol
Watershed
(Source: Personal Calculations, 2024)
Figure 7. Map of Soil Types of Grompol
Watershed
(Source: Personal Calculations, 2024)
Based on these two figures, the calculation of compos
ite CN and adequate rain is then carried out,
where, for the soil class, the soil class most commonly used is soil class D.
The calculation of composite CN can be seen in Table 10.
Table 10. Calculation of
Composite CN
Land Use |
Soil Classification |
Broad |
CN x Area |
||
BIG |
CN |
Soil Type |
CN Value |
km2 |
|
Plantations/Gardens |
Soil with Conservation |
D |
91 |
11,73 |
1067,24 |
Tegalan/Farm |
91 |
20,12 |
1830,64 |
||
Sawah |
91 |
79,53 |
7237,41 |
||
Rainfed Rice Fields |
91 |
0,44 |
40,45 |
||
Building/Building |
Settlement |
D |
84 |
0,06 |
5,17 |
Settlements and Activity Places |
84 |
49,62 |
4167,70 |
||
Meadow |
Grassland (Good Condition) |
D |
78 |
0,65 |
50,52 |
Bushes |
Grassland (Poor Condition) |
D |
89 |
2,30 |
205,09 |
Sum |
|
699 |
164,45 |
14604,23 |
(Source: Personal Calculations, 2024)
CNk =
= = 88,81
Maximum potential retention (S) = = = 32,02 mm
t = 1 jam
P = 19,62 mm
ΣP = 19,62 mm
ΣPeff = = = 3,86 mm
Peff = ΣPeff (i) - ΣPeff (i - 1) = 3,86 – 0 = 3,86 mm
The full results of the practical rain calculation can be seen in Table 11.
Table 11. Effective Rainfall
Calculation
t |
P |
ΣP |
ΣP eff |
P eff |
1 |
19,62 |
19,62 |
3,86 |
3,86 |
2 |
107,58 |
127,20 |
95,49 |
91,63 |
3 |
27,96 |
155,16 |
122,41 |
26,93 |
4 |
15,62 |
170,77 |
137,57 |
15,16 |
Σ |
170,77 |
|
Σ |
137,57 |
(Source: Personal Calculations, 2024)
Based on Table 11, the practical rainfall value
obtained with the SCS-CN method for the first hour was 3.86 mm, the second hour
was 91.63 mm, the third hour was 26.93 mm, and the fourth hour was 15.16 mm.
g) Nakayasu Synthesis Unit Hydrograph Method
The Nakayasu Synthesis Unit
Hydrograph Method was developed by its inventor in Japan based on several
rivers in Japan
Watershed area (A) = 164,95 km2
Length of Main River (L) = 54,83 km
King = 1 mm
tg = = 0,4 + 0,058 . 54,83
= 3,58 hours
Tr = 0,75. 3,58 =
2,68 hours
Tp = = 3,58 + 0,8. 2,68 = 5,73
T0,3 = = 2 . 3,58 = 7,16
Qp = = 5,16 m3/s
The hydrograph parameters of the Nakayasu unit above are used to calculate the coordinates of the hydrograph several times (t) as follows:
On an upward curve (0 < t < 5,7)
Qt initial
=
On the downward curve (5,73 < t <
12,89)
Qt initial
=
On the downward curve
(12,89 < t < 23,63)
Qt initial
=
On the downward curve (t < 23,63)
Qt initial =
The results of the
Nakayasu Unit Hydrograph can be seen
in Figure 8.
Figure
8. Nakayasu Unit Hydrograph
(Source: Personal Calculations, 2024)
Next, the flood hydrograph
value is calculated, where the flood hydrograph
value is the amount of
direct runoff hydrograph with the bottom flow.
Watershed area (A) = 164,95 km2
Length of rivers of
all levels = 612,26 km
Drain tissue density (D) = = 3,71
Base Flow (BF)
BF = 0,4751 A0,6444
D0,9430
BF = 0,4751.
(164,95)0,6444. (3,71)0,9430 = 43,93 m3/s
The results of the
Nakayasu Flood Hydrograph can be seen in Figure
9.
Figure
9. Nakayasu Flood Hydrograph
(Source: Personal Calculations, 2024)
Based on the calculation step with the Nakayasu Method,
the planned flood discharge value in the Grompol
watershed for the 25-year renewal period was 623,32 m3/s.
Conclusion
Based on the results of the analysis and discussion in this study, the following conclusions can be drawn: (1) The problems that occur in the Grompol River are the presence of sediment, organic waste, and inorganic waste. (2) The flow of the Grompol River has been flooded at 4 points out of 31 survey locations, namely in the settlements around the Gedangan Lor Bridge, the Gading Grompol Bridge, the Gantung Kedusan Bridge, and the Pringanom Bridge, where flood control efforts from the government and local communities are dominated in the form of community service. (3) The area of the Grompol watershed using QGIS 3.10.6 Software is 164,95 km2. (4) The amount of planned flood discharge in the Grompol watershed with a re-period of 25 years using the Nakayasu Synthesis Unit Hydrograph Method is 623,32 m3/s.
BIBLIOGRAPHY
Andayani, R., & Umari, Z. F. (2022). Debit Banjir
Rancangan DAS Selabung dengan HSS Nakayasu. Jurnal Deformasi, 7(1),
21. https://doi.org/10.31851/deformasi.v7i1.7803
Ardana, P. D. H., Soriarta, K., Widnyana, I. G. A., & Diasa, I. W. (2021). Analisis Debit Banjir Rancangan di Daerah Aliran Sungai Tukad Mati Studi Kasus: Daerah Aliran Sungai Tukad Mati. Jurnal Teknik Gradien, 13(2), 58–70. https://doi.org/10.47329/teknikgradien.v13i2.761
Ayuni, T. P., Saputra, A. J., & Ginting, J. M. (2023). Analisis Banjir Metode Hidrograf Satuan Sintetis SCS dan Nakayasu DAS Pesung, Batam. Jurnal Ilmiah Rekayasa Sipil, 20(2), 146–155. https://doi.org/10.30630/jirs.v20i2.1031
Badan Standarisasi Nasional. (2016). SNI 2415 : 2016 Tata Cara Perhitungan Debit Banjir Rencana.
Bambang Triatmodjo. (2013). Hidrologi Terapan (3rd ed.). Beta Offset.
Cambodia, M., Hasan, Moch. I., & Novilyansa, E. (2022). Analisis Debit Banjir Rancangan Menggunakan Metode HSS Nakayasu di Sungai Tulang Bawang Provinsi Lampung. Prosiding Seminar Nasional Penelitian Dan Pengabdian Kepada Masyarakat, 2(1), 92–96. https://doi.org/10.24967/psn.v2i1.1489
Fauziyah, S., Sobriyah, & Susilowati. (2013). Analisis Karakteristik dan Intensitas Hujan Kota Surakarta. Matriks Teknik Sipil, 1(1), 82–89.
Id’fi, G. (2020). Analisa Model Hidrograf Banjir Kali Ngotok dengan Metode SCS, Snyder dan Nakayasu. BANGUNAN, 25(2), 1. https://doi.org/10.17977/um071v25i22020p1-10
Ifginia, I. (2020). Analisis Debit Banjir Rencana Sungai Palu dengan Menggunakan Hidrograf Satuan Sintetik (HSS) Nakayasu. Jurnal Teknik Sipil, 11(2), 1195. https://doi.org/10.36448/jts.v11i2.1545
Miradj, A., & Rahman, S. (2020). Analisis Debit Banjir Sungai Uru Ino, Kabupaten Halmahera Timur Menggunakan Pendekatan Hidrograf Satuan Sintetis (Hss) Gamma I Dan Hss Nakayasu. Dintek, 13(1), 1–13.
Mulyandari, E., & Susila, H. (2020). Validasi Data Curah Hujan Satelit Trmm Dan Persiann Dalam Analisis Debit Banjir Rencana Di Das Telaga Lebur. Jurnal Teknik Sipil Dan Arsitektur, 25(2), 16–22. https://doi.org/10.36728/jtsa.v25i2.1070
Mulyandari, E., Wijayanti, P., & Gunarso. (2024). Hidrologi Terapan : Prinsip dan Aplikasi Hidrologi dalam Manajemen Lingkungan dan Infrastruktur. In Penamuda Media.
Saputra, A., & Saputri, U. S. (2021). Analisa Debit Banjir Rencana dengan Metode Hidograf Satuan Sintetis Nakayasu di Daerah Aliran Sungai Cimandiri. Jurnal TESLINK : Teknik Sipil Dan Lingkungan, 3(1), 01–10. https://doi.org/10.52005/teslink.v2i1.61
Sri Harto BR. (2022). Analisis Hidrologi. PT Gramedia Pustaka Utama.
Sulhan, R. A., Efendi, M., & Hapsari, R. I. (2020). Analisis Debit Banjir pada Sungai Buntung di Kabupaten Sidoarjo. Jurnal JOS-MRK, 1(3), 79–84. https://doi.org/10.55404/jos-mrk.2020.01.03.79-84
Suripin. (2004). Drainase Perkotaan yang Berkelanjutan. Andi Offset.
Syarifudin, M., & Utomo, K. S. (2020). Perbandingan Perkiraan Debit Puncak Banjir Menggunakan Metode Nakayasu dan Metode FSR Jawa Sumatera untuk DAS Dombo Sayung. Reka Buana : Jurnal Ilmiah Teknik Sipil Dan Teknik Kimia, 5(2), 38. https://doi.org/10.33366/rekabuana.v5i2.1894
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