Syntax Literate: Jurnal Ilmiah Indonesia p�ISSN: 2541-0849
e-ISSN : 2548-1398
Vol. 6, No. 10, Oktober 2021
Nugroho Widiasmadi
Faculty of Engineering, Wahid Hasyim Universitas, Semarang, Jawa Tengah, Indonesia
Email:
[email protected]
Abstract
This research was
conducted on Humus soils, especially for Corn Plantation, aimed at restoring
soil health and fertility due to the use of chemical fertilizers and
pesticides. Through controlled microbial activity through bio whole. This study
observes periodically changes in soil acidity, infiltration rate, and
electrolyte conductivity levels around the center of the biohole as the center
of the microbial distribution. As a comparison, observations were made using a biohole
that was only filled with water without microbes. Furthermore, these two
conditions, namely biohole with microbes and biohole without microbes, were
compared to changes in parameters: soil acidity, infiltration rate, and
electrolyte conductivity levels. So that it can be seen a real difference in
the speed of improvement of the two soil conditions and the ability of the soil
to provide nutrients during vegetative and generative growth. Soil carrying
capacity research using microbial activity variables as a measurable control is
called Biosoildam Technology. This research was conducted on agricultural land
with commodities as above. The tools used are the Double Ring Infiltrometer to
measure the infiltration rate at three radial distances from the center of the
microbial hole (Biohole), the measurement of electrolyte salt content as an
indication of soil fertility using Electrolyte Conductivity, and the use of a
PH meter as a measure of soil acidity. Infiltration calculations were carried
out every 5 minutes and observed every 15 days for 45 days.� This research is expected to: reduce
production costs, increase crop yields, make agriculture sustainable, produce
multiplayer economies of effect, strengthen crops to face global climate
change. The result of the research shows that the highest infiltration
rate,� infiltration capacity, fertility
& acidity happened on soil involving Biofertilizer MA-11, ie 83-99 cm/hour,
325 � 970 uS/cm, PH = 6- 6,5. While the lowest infiltration rate,� infiltration capacity, fertility &
acidity was happened on soil without involving Alfaafa Microba MA-11, ie 31- 52
cm/hour, 325 � 540 uS/cm, PH 5 � 6
Keywords: humus; biohole; infiltration; biosolid; land use;
Alfalfa Microba; fertility; acidity
One of the main contributing factors is a decrease in fertility, health, and soil absorption (infiltration rate) triggered by excessive use of inorganic fertilizers (pesticides) (Widiasmadi, 2019), the ecological function of absorbing rainwater RTH is an area planted with trees and grass that can improve soil structure so that the rate of rainwater infiltration can be maintained (Budi, 2016). The place is around reservoirs or lakes that can minimize water runoff on the surface when it rains (Rochim & Syahbana, 2013). According to (Yohana, Griandini, & Muzambeq, 2017), one of the environmentally friendly technological solutions in overcoming the availability of groundwater is by making bio pure infiltration holes, namely technological engineering for water absorption in the form of vertical and effective cylindrical holes (Martha, 2018), and according to LRB also by impregnating and reducing the overflow of rainwater can minimize the occurrence of flooding (Latifah, 2012). In addition, according to (Widyastuti, 2013), one method to reduce the accumulation of organic waste is to turn it into compost. However, according to (Santosa, 2018), fruit waste causes a higher water infiltration rate than vegetable or leaf waste. Infiltration is the process of water flowing into the soil which generally comes from rainfall, while the infiltration rate is the amount of water that enters the soil per unit of time. This process is a very important part of the hydrological cycle which can affect the amount of water that is on the surface of the soil. Water on the surface soil will enter the soil and then flow into the river (Sunjoto, 2011). Not all surface water flows into the soil, but some portion of the water remains in topsoil to be further evaporated back into the atmosphere through the soil surface or soil evaporation (Eng & Dr, 2004).
Infiltration capacity is the ability of the soil to absorb large amounts of water into the ground and is influenced by the microorganism activities in the soil (Nugroho Widiasmadi, 2020). The large infiltration capacity can reduce surface runoff. The reduced soil pores, generally caused by soil compacting, can cause a decreased infiltration. This condition is also affected by soil contamination (Dr, 2020) due to excessive use of chemical fertilizers and pesticides which hardens the soil as well.
Biosoildam is a Biodam technology that involves microbial activity in increasing the measured and controlled inflation rate. Biological activities through the role of microbes as agents of biomass decomposition and soil conservation become important information for soil conservation efforts in supporting healthy food security.
Increased soil friability by involving microbial activities (Bioinfiltrosoil) can be used as the development of the science of Civil Hidro Engineering as Eco-Civil Engineering. So that engineering can provide value to the carrying capacity of land productivity through soil and water conservation (Widiasmadi, 2019).
Method
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�� Figure 4 Corn Plantation |
a.
Catalytic Discharge
Biosoildam
innovation uses runoff discharge as a media for biological agents distribution
through the inlet/inflow (Biohole) as a center for
the microbial population's distribution with water. The runoff discharge
calculation as a basis for the Inflow Biosoildam
formula requires the following stages:
1. conducting a rainfall analysis,
2. calculating the catchment area, and
3.
analyzing
the soil/rock layers.
Biosoildam
structure can be made with holes in the soil layer without or using water
pipes/reinforced concrete pipes (RCP) with a perforated layer that will let
microbes spread radially. We can calculate the discharge entering Biohole as a function of the catchment characteristic with
a rational formula:
Q = 0,278
CIA���������� ������������������������������������������������������������������������������������������(1)
where C is the runoff
coefficient value, I is the precipitation and A is the area (Sunjoto, 2011). Based on this formula, the Table presents the results of
runoff discharge.
b.
Infiltration
Infiltration is the process by which
water on the ground surface enters the soil.
It is commonly used in both hydrology and soil sciences. The infiltration
capacity is defined as the maximum rate of infiltration. It is most often
measured in meters per day but can also be measured in other units of distance
overtime if necessary. The infiltration capacity decreases as the soil
moisture content of soils surface layers increases. If the precipitation rate exceeds the infiltration
rate, a runoff will usually occur unless
there is some physical barrier. Infiltrometers, parameters, and
rainfall simulators are all devices that can be used to measure infiltration
rates. Infiltration is caused by multiple factors including; gravity, capillary
forces, adsorption, and osmosis. Many soil characteristics can also play a role
in determining the rate at which infiltration occurs.
The spread of microbes as a biomass
decomposing agent can be controlled through the calculation of the infiltration
rate at several point radii from Biohole as the center
of the spread of microbes. by using the Horton method. Horton observed that
infiltration starts from a standard value fo and
exponentially decreases to a constant condition FC. One of the earliest
infiltration equations developed by Horton is:
f(t)
= FC + (fo
� FC)e-kt�����������������������������������������������������������������
(2)
where :
k is a constant reduction to the
dimension [T -1] or a constant decreasing infiltration rate.
fo
is an infiltration rate capacity at the beginning of the measurement.
FC is a constant infiltration capacity
that depends on the soil type.
The fo and FC
parameters are obtained from the field measurement using a double-ring
infiltrometer. The fo and FC parameters are the
functions of soil type and cover. Sandy or gravel soils have high values, while
bare clay soils have little value, and for grassy land surfaces, the value increases
(Sutanto, 2012).
The infiltration calculation data from
the measurement results in the first 15 minutes, the second 15 minutes, the
third 15 minutes, and the fourth 15 minutes at each distance from the center of
Biohole are converted in units of cm/hour with the
following formula:
Infiltration rate = (ΔH/t x 60)������������������������������������������������������������������
���(3)
where:
ΔH = height decrease (cm) within a certain time interval,
T = the time interval required by water in ΔH to enter the ground (minutes) (Zhanbin, Lun, Suiqi, & Pute, 1997). This observation takes place every 3 days for one month.
c. Soil Characteristics
The porosity of soils is critical in determining the
infiltration capacity. Soils that have smaller pore sizes, such as clay, have
lower infiltration capacity and slower infiltration rates than soils that have
large pore sizes, such as sands. One exception to this rule is when the clay is
present in dry conditions. In this case, the soil can develop large cracks
which lead to higher infiltration capacity.
Soil compaction is also impacted infiltration capacity.
Compaction of soils results in decreased porosity within the soils, which
decreases infiltration capacity.
Hydrophobic soils can develop after wildfires have happened, which can greatly diminish or completely prevent infiltration from occurring.
Organic
materials in the soil (including plants and animals) all increase the
infiltration capacity. Vegetation contains roots that extend into the soil
which create cracks and fissures in the soil, allowing for more rapid
infiltration and increased capacity. Vegetation can also reduce surface
compaction of the soil which again allows for increased infiltration. When no
vegetation is present infiltration rates can be very low, which can lead to
excessive runoff and increased erosion levels. Similar to vegetation, animals that
burrow in the soil also create cracks in the soil structure.
d.
Microbial Population
This analysis uses MA-11 biological
agents that have been tested by the Microbiology Laboratorium of Gadjah Mada
University based on Ministerial Regulation standards: No 70/Permentan/SR.140/10
2011, includes:
Table 1
Microbes Analysis
No |
�Population Analysis |
Result |
No |
�Population Analysis |
Result |
1 |
Total of Micobes |
18,48 x 108cfu |
8 |
Ure-Amonium-Nitrat Decomposer |
Positive |
2 |
Selulotik Micobes |
1,39 x 108cfu |
9 |
Patogenity� for plants |
Negative |
3 |
Proteolitik Micobes |
1,32 x 108cfu |
10 |
Contaminant E-Coly & Salmonella |
Negative |
4 |
Amilolitik Micobes |
7,72 x 108cfu |
11 |
Hg |
2,71 ppb |
5 |
N Fixtation Micobes |
2,2 x 108cfu |
12 |
Cd |
<0,01 mg/l |
6 |
Phosfat Micobes |
1,44 x 108cfu |
13 |
Pb |
<0,01 mg/l |
7 |
Acidity |
3,89 |
14 |
As |
<0,01 ppm |
(resource : (Widiasmadi, 2019)
Its application in Biosoildam is
concentrating the microbes into "population media", as a source of
soil conditioner for increasing infiltration rates and restoring natural fertility
(Nugroho Widiasmadi,
2020).
e.
Soil Fertilizer & �Soil Acidity
Microbial activity as a contributor
to soil nutrition from the biomass decomposition results can be controlled
through the salinity level of the nutrient solution expressed through
conductivity as well as other parameters as analog inputs. Conductivity can be
measured using EC, Electroconductivity, or Electrical (or Electro) Conductivity
(EC) is the nutrients density in solution. The more concentrated the solution
is, the greater the delivery of electric current from the cation (+) and anion
(-) to the anode and cathode of the EC meter. Thus, it results in a higher EC.
The measurement unit of EC is mS/cm (millisiemens) (Nugroho Widiasmadi, 2020).
Indications of microbial activity on
fertility can be controlled through acidity. The number of nutrients contained
in the soil is an indicator of the level of soil fertility due to the activity
of biological agents in decomposing biomass. Important factors that influence
the absorption of nutrients (EC) by plant roots are the degrees of soil acidity
(soil pH), temperature (T), and humidity (M). Soil Acidity level (pH) greatly
influences the plant�s growth rate and development (Widiasmadi, 2019).
Infiltration Rate cm/ hour |
��������������������������� Time
(minute) |
Infiltration
Rate cm/ hour |
������������������������������� Time (minute) |
Infiltration
Rate cm/ hour |
�������������������� Time (minute) |
Infiltration
Rate cm/ hour |
��������������������� Time
(minute) |
Infiltration
Rate cm/ hour |
���������������������������������������
Time (minute) |
Microbial distribution in this case that is the Humus soil layer is
quite effective at a maximum radius of 2 meters with a distance between Bioholes of 5 meters and even the spread of the microbes
can be even further. The use of microbes in the infiltration well system or the
biosolid method as a biological agent is very effective, especially to increase
the productivity of barren land into fertile land in a measurable manner so
that it does not merely include water. Biosoildam
method still needs to be tested for various lands with various rock soil
formations so that the relationship between the soil permeability level and the
concentration value of microbial population involved for a fertility target of
an area to be a productive land is acquired. Biosoildam
can be called the "Active Infiltration System" since it involves
microbial activities that can be useful for 1). Expanding soil porosity that
increases oxygen content as a source of soil health. 2). Increasing macro and
micro soil nutrient content of the biomass elements that the microbes break
down in the distribution zones from the biohole center.
3). Repairing saturated soils that have long been contaminated with chemical
fertilizers and pesticides by microbial degradation.
Budi, Basuki Setiyo. (2016). Model
Peresapan Air Hujan Dengan Menggunakan Metode Lubang Resapan Biopori (Lrb) Dalam
Upaya Pencegahan Banjir. Wahana Teknik Sipil: Jurnal Pengembangan Teknik
Sipil, 18(1). Google Scholar
Douglas, M. G. (1988). Integrating
Conservation Into Farming Systems: The Malawi Experience. Google Scholar
Dr, Nugroho Widiasmadi.
(2020). Analysis Of Soil Fertlity And Acidity In Real Time Using Smart
Biosoildam To Improe Agricultural Land: International Journal Of Research And
Analytical Reviews (Ijrar). Volume, 7, 194�200. Google Scholar
Eng, Suripin Dr Ir M., &
Dr, Suripin Ir. (2004). Sistem Drainase Perkotaan Yang Berkelanjutan. Andi
Offset, Yogyakarta. Google Scholar
Latifah, Riris Nurul Nurul.
(2012). Pemanfaatan Sampah Organik Sebagai Bahan Pupuk Cair Untuk Pertumbuhan
Tanaman Bayam Merah (Alternanthera Ficoides). Lenterabio: Berkala Ilmiah
Biologi, 1(3), 139�144. Google Scholar
Martha, Luluk. (2018). Studi
Resapan Air Hujan Melalui Lubang Resapan Biopori (Lrb) Sebagai Upaya Mereduksi
Beban Drainase Di Universitas Islam Negeri Sunan Ampel Surabaya. Uin Sunan
Ampel Surabaya. Google Scholar
Rochim, Faidloh Nur, &
Syahbana, Joesron Alie. (2013). Penetapan Fungsi Dan Kesesuaian Vegetasi Pada
Taman Publik Sebagai Ruang Terbuka Hijau (Rth) Di Kota Pekalongan (Studi Kasus:
Taman Monumen 45 Kota Pekalongan). Teknik Pwk (Perencanaan Wilayah Kota),
2(3), 314�327. Google Scholar
Santosa, Slamet. (2018).
Effect Of Fruits Waste In Biopore Infiltration Hole Toward The Effectiveness Of
Water Infiltration Rate On Baraya Campus Land Of Hasanuddin University. Journal
Of Physics: Conference Series, 979(1), 12037. Iop Publishing. Google Scholar
Sunjoto, S. (2011). Teknik
Drainase Pro-Air. Yogyakarta: Fakultas Teknik Universitas Gadjah Mada. Google Scholar
Sutanto. (2012). Desain Sumur
Peresapan Air Hujan. In Laporan Penelitian. Yogyakarta : Fakultas
Geografi Universitas Gadjah Mada. Google Scholar
Widiasmadi, Nugroho. (2019).
Peningkatan Laju Infiltrasi Dan Kesuburan Lahan Dengan Metode Biosoildam Pada
Lapisan Tanah Keras Dan Tandus. Prosiding Snst Fakultas Teknik, 1(1). Google Scholar
Widiasmadi, Nugroho. (2020a).
Analisa Elektrolit Konduktifitas & Keasaman Tanah Secara Real Time
Menggunakan Smart Biosoildam. Prosiding Seminar Nasional Nciet, 1(1),
11�24. Google Scholar
Widiasmadi, Nugroho. (2020b).
Soil Improvement And Conservation Based In Biosoildam Integrated Smart Ecofarming
Technology (Applied In Java Alluvial Land And Arid Region In East Indonesia). Int
J Innov, 5(9). Google Scholar
Widyastuti, Sri. (2013).
Perbandingan Jenis Sampah Terhadap Lama Waktu Pengomposan Dalam Lubang Resapan
Biopori. Waktu: Jurnal Teknik Unipa, 11(1), 5�14. Google Scholar
Yohana, Corry, Griandini,
Dientje, & Muzambeq, Said. (2017). Penerapan Pembuatan Teknik Lubang
Biopori Resapan Sebagai Upaya Pengendalian Banjir. Jurnal Pemberdayaan
Masyarakat Madani (Jpmm), 1(2), 296�308. Google Scholar
Zhanbin, Huang, Lun, Shan,
Suiqi, Zhang, & Pute, Wu. (1997). Action Of Rainwater Use On Soil And Water
Conservation And Agriculture Sustainable Development [J]. Bulletin Of Soil
And Water Conservation, 1. Google Scholar
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