dampak lingkungan akibat sampah
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PERMASALAHAN LINGKUNGAN AKIBAT
SAMPAH
KESEHATAN LINGKUNGAN/MASYARAKAT
KUALITAS LINGKUNGANFISIKO-KIMIA
KUALITAS LINGKUNGAN
BIOLOGI
SAMPAH = BAHAN YANG TIDAK
BERGUNA
SAMPAH = SUMBERDAYA
EKONOMI
BUANGLAH SAMPAH PADA TEMPATNYA
KUMPULKAN SAMPAH PADA TEMPATNYA
PENCEMARAN UDARA AKIBAT SAMPAH
BAU BUSUK ASAP ,
BIO-GAS -BERBAHAYA
1. Tetra kloro etilen & kloroform : Feto-toksik2. Benzene & Metil-etil-keton : Embrio-toksik3. Metilen-klorida, Kloro-benzene: Perkembangan janin4. CH4 ------ CO2 ------ H2CO3 NH3 ------ NH4NO3 Hujan Asam H2S ------ H2SO45. Bau Busuk sampah : Dampak emosional masyarakat
Kurva fungsional O & VIndeks Kualitas
1.0
0.8
0.6
0.4
0.2
0.0 Visual Quality Heavy Moderate Clear pollution
KUALITAS UDARA: ODOR & VISUAL
sampah
Pleasant odor
Lacking odor
disagreeable
Kurva fungsional (Microscale)Indeks Kualitas
1.0
0.8
0.6
0.4
0.2
0.0 100 200 300 400 Rataan 24 jam ( g/m3)
KUALITAS UDARA: PARTIKULAT
sampah
Kurva fungsional (Microscale)Indeks Kualitas
1.0
0.8
0.6
0.4
0.2
0.0 0.1 0.2 0.3 0.4 Rataan 3 jam (06.00 - 09.00), ppm
KUALITAS UDARA : HIDROKARBON
sampah
Kurva fungsional (Microscale)Indeks Kualitas
1.0
0.8
0.6
0.4
0.2
0.0 10 20 30 40 50 Konsentrasi 1 jam , ppm
KUALITAS UDARA : CARBON MONOKSIDA
sampah
Kurva fungsional (Microscale)Indeks Kualitas
1.0
0.8
0.6
0.4
0.2
0.0 0.05 0.10 0.15 Annual average , ppm
KUALITAS UDARA : OKSIDA NITROGEN
sampah
SAMPAH
DEKOMPOSISI
LINDI (LEACHATE)
MENYUMBAT SALURAN AIR
BOD - CODNITROGEN
FOSFATPENCEMARAN AIR
BANJIR
SIKLUS KARBON
CO2 UDARA
C Anorganik C Fitoplankton
C-organik soluble
(Detritus)
C Zooplankton
C Sedimen
C-organik suspend.(Detritus)
SAMPAH
KISARAN DO DALAM AIR NORMAL: 7.1 - 14.6 ppm
Kurva fungsional DO
Indeks Kualitas1.0
0.8
0.6
0.4
0.2
0.0 2 4 6 8ppm DO
9 ppm : jenuh
Sampah
Kurva fungsional BOD
Indeks Kualitas1.0
0.8
0.6
0.4
0.20.0 10 20 30 40 50 60 70
ppm BOD
waduk
KUALITAS AIR: BOD
Sungai
Sampah
Kurva fungsional Kadar N-anorganik
Indeks Kualitas1.0
0.8
0.6
0.4
0.2
0.0 1 2 4 6 8 10
ppm N
KUALITAS AIR: N- ANORGANIK
Sampah
SIKLUS P DALAM PERAIRAN
Jaringan
tanaman
Jaringan
binatang
DIPP-
anorganik larut
Batuan
fosfat
SEDIMEN Jaringan
Bakteri
POP & DOPparticulate &
dissolved
SAMPAH
Kurva fungsional Kadar P-anorganikIndeks Kualitas
1.0
0.8
0.6
0.4
0.2
0.0 0.02 0.04 0.06 0.08 0.10 ppm P
KUALITAS AIR: FOSFAT- ANORGANIK
sampah
Kurva fungsional TURBIDITASIndeks Kualitas
1.0
0.8
0.6
0.4
0.2
0.0 20 40 60 80 100 120 140 Satuan Turbiditas Jackson
KUALITAS AIR: TURBIDITAS
sampah
Kurva fungsional ColiformIndeks Kualitas
1.0
0.8
0.6
0.4
0.2
0.0 101 102 103 104 105 106 MPN/100 ml
KUALITAS AIR: COLIFORM
sampah
Kurva fungsional Indeks Kualitas
1.0
0.8
0.6
0.4
0.2
0.0 None Light Moderate Heavy Floating material
KUALITAS AIR: ODOR & FLOATING MATERIAL
sampah
Lacking odor
Noticeable
Disagreeable
Kurva fungsional Indeks Kualitas
1.0
0.8
0.6
0.4
0.2
0.0 Static Slow Moderate Whitewater Flow characteristics
KUALITAS ESTETIKA AIR: Water appearance
sampah
Moderate turbid
Clear
Turbid
GANGGUAN KESEHATAN LINGKUNGAN
SAMPAHSAMPAH
TIKUS
LALAT, NYAMUK
KECOAK
CACING
MIKROBA
VEKTOR / PATOGEN ----- GANGGUAN PENYAKIT
DAUR ULANG SAMPAH ANORGANIK
Kertas, kardus, karet, plastik, gelas, logam, dll
BERNILAI EKONOMI
Bahan baku proses produksi Produk X
PRODUK X
Bahan baku Proses produksi Produk Y
PRODUK Y
MENGURANGI SUMBER SAMPAH
RECYCLING
USE & REUSE
REKLAMASIPRODUCT CHANGE
SOURCE CONTROL
INPUT MATERIAL CHANGE
GOOD OPERATING PRACTICES
TECHNOLOGY CHANGE
PENGELOLAAN SAMPAH adalah pengumpulan , pengangkutan , pemrosesan , pendaur-
ulangan , atau pembuangan dari material sampah.
Pengertian ini biasanya mengacu pada material sampah yg dihasilkan dari kegiatan manusia, dan biasanya dikelola untuk mengurangi dampaknya terhadap kesehatan, lingkungan atau
keindahan.
Pengelolaan sampah juga dilakukan untuk memulihkan sumber daya alam .
Pengelolaan sampah bisa melibatkan zat padat , cair , gas , atau radioaktif dengan metoda dan keahlian khusus untuk masing
masing jenis zat.
Hierarchy of Waste Management
http://www.envirocentre.ie/Content.aspx?ID=96448806-bc07-4f5a-9e67-cb684d985609&PID=518accea-eec4-
4cdf-b034-78ce58eacb4d
The EU concept of a waste management hierarchy,
whereby waste prevention and re-use are viewed as the most desirable options for managing wastes with the
least desirable option considered being landfill.
The overall intent of these policy statements is to move
Irish waste management away from landfill into those
options that feature in the upper echelons of the
hierarchy.
DOMESTIC WASTES AND WATER POLLUTION
Domestic waste is classified as a point source of pollution, because the wastewater from homes and
commercial establishments is often directly emitted into bodies of
water. Domestic waste can vary from
cleaning products, to household things used by regular people.
These pollutants can pose a high risk on a large scale. When these
domestic liter is mixed in with the clean environment, the pollution and our water can be combined
into a very deadly mix.
http://t3-1contaminant.blogspot.com/2010/03/introduction-water-is-essential-to-our.html
Effects of water pollution are the death of marine organisms in rivers and oceans (this may be due to lack of oxygen, destruction of habitat, not enough food, lack of sunlight, etc.). When our waters are polluted, this can threaten our
living.
Many diseases will come with drinking unpure- water or swimming in toxic water. Such health problems may be blood disease, heart disease, nervous system disorders,
diarrhea, skin lesions, and vomiting in humans.
DOMESTIC WASTES AND WATER POLLUTION
http://t3-1contaminant.blogspot.com/2010/03/introduction-water-is-essential-to-our.html
Eutrophication occurs when large quantities of nutrients such as
nitrates and phosphates enter an aquatic environment. Sources of these nutrients include animal
wastes, agricultural runoff, and sewage. The ecosystem quickly
experiences an increase in photosynthetic and blue-green
algae, as these organisms thrive in the presence of the added
nutrients. An algae bloom occurs as the algae accumulates into dense, visible patches near the
surface of the water, prohibiting light from penetrating deeper
areas of lake or stream. Some fish are unable to survive without this light, but for them an even more serious problem arises when the
algae begin to die.
http://library.thinkquest.org/04oct/01590/pollution/eutrophication.html
CONTROLLING EUTROPHICATION
The following is a list of methods that can be used to control eutrophication:
1.planting vegetation along streambeds to slow erosion and absorb nutrients2.controlling application amount and timing of fertilizer 3.controlling runoff from feedlots4.researching use of biological controls; for example, the process of denitrification uses specialized bacteria that convert nitrates to harmless molecular nitrogen