tugas kultur sel - makro dan mikro nutrien
TRANSCRIPT
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Micronutrients
The micronutrients that are managed by growers and we will discuss include:
• Iron
• Boron
• Manganese
• Zinc
• Molybdenum
• Cobalt
There are three additional micronutrients that have been classified as essential, but are generally not managed
by growers. These additional three nutrients, listed below, are rather managed under exerimental conditions:
• !ic"el
• Chlorine
• Cobalt
Forms and Functions of Micronutrients
IRON
•Form: Iron is ta"en u by lants as either #e
$%
&ferrous cation' or #e(%
&ferric cation'.
• Function: Iron is involved in hotosynthesis, resiration, chlorohyll formation, and many en)ymatic
reactions.
BORON
• Form: Boron is ta"en u by lants rimarily as *(B+( &boric acid' and *$B+( &borate'.
•
Function: Boron lays an imortant role in the movement and metabolism of sugars in the lant and
synthesis of lant hormones and nucleic acids. It also functions in lignin formation of cell walls.
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MANGANESE
• Form: The rimary form of manganese uta"e is Mn$% &manganous ion'.
• Function: Manganese is a comonent of en)ymes and is also involved in hotosynthesis and root
growth. -dditionally, it is involved in nitrogen fixation.
ZINC
• Form: The Zn$% cation is the redominate form ta"en u by lants.
• Function: Zinc is a comonent of many organic comlexes and !- rotein. It is also an imortant
en)yme for rotein synthesis. -lso, )inc is involved in growth hormone roduction and seed
develoment.
MOLYBDENUM
• Form: Molybdenum is rimarily ta"en u as Mo+/$ &molybdate ion'.
• Function: It is involved in nitrogen fixation &conversion of !$ to !*/%' and nitrification &conversion of
!*/% to !+(
'.
COPPER
• Form: Coer is ta"en u as Cu$% &curic ion'.
• Function: Coer is also a comonent of en)ymes, some of which are imortant to lignin formation in
cell walls. It is also involved in hotosynthesis, resiration, and rocesses within the lant involving
nitrogen.
Cycling:
IRON
The iron cycle includes both mineral and organic forms.
Mineral Iron
Iron may exist:
• in the soil solution
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o includes soluble iron and organic matter comlexes in the form of chelates
• as rimary minerals and0or reciitated minerals
• cation exchange site on soil articles
#e containing minerals may dissolve to relenish the soil solution as iron is removed by lants. 1ittle iron is
retained by the cation exchange sites of soil articles as comared to base and acid cations.
Organic Iron
+rganic cycling is an imortant rocess that ensures iron availability through the rocesses of minerali)ation and
immobili)ation.
Iron Chelation
Iron can also form strong comlexes with organic matter "nown as chelates &a 2ree" word meaning 3claw4'.
Chelation occurs between soluble organic comounds and certain metals in the soil through rocesses involving
microorganisms. Chelates are very imortant in micronutrient management because chelation increases the
solubility and lant uta"e of many metal micronutrients. 5e will encounter chelation again when discussing )inc,
coer and manganese.
MANGANESE
The manganese cycle is very similar to the iron cycle. The manganese cycle, too, has four fractions:
• manganese cations in soil solution
o includes soluble manganese and organic matter comlexes "nown as chelates
•
exchangeable manganese on soil articles &cation exchange sites'
• rimary and secondary manganesecontaining minerals
• soil organic matter
1i"e iron, little manganese is retained by the cation exchange sites of soil articles. Manganese may undergo
reciitation0dissolution, sortion0desortion on the C6C, minerali)ation0immobili)ation, and chelation.
ZINC
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Zinc cycling includes:
• )inc cations in soil solution )inc
o includes soluble )inc and organic matter comlexes "nown as chelates
• )inc retained by soil articles on the cation exchange sites
• rimary and secondary )inccontaining minerals
• soil organic matter
Zinc bearing minerals can dissolve and suly )inc to the soil solution. +nce in the soil solution, )inc can be
immobili)ed, ta"en u by lants, retained by soil articles, or chelated with soluble organic matter. +rganic matter
containing )inc must undergo minerali)ation before it becomes available for lant uta"e.
COPPER
1i"e Zinc, the coer cycle includes:
• 7olution coer
o Includes soluble coer and organic matter comlexes "nown as chelates
• 6xchangeable coer on the cation exchange sites of soil articles
• 8rimary and secondary coer minerals
o Coer may be occluded, or buried, within the structures of various minerals, such as iron and
aluminum oxides
• +rganic coer
o Coer is more tightly bound to organic matter than the other micronutrients
o Coer deficiencies can occur in organic soils
Coercontaining minerals can dissolve and suly Zn to the soil solution. 1i"e )inc, coer can be immobili)ed
by microorganisms, ta"en u by lants, or exchanged on soil article surfaces. Coer may also form chelates
with soluble organic matter. +rganic coer must be minerali)ed before it is available for lant uta"e.
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MOLYBDENUM
9nli"e the revious metal micronutrients, molybdenum exists as an anion in the soil solution. !onetheless, the
molybdenum cycle is similar to the others. The molybdenum cycle includes:
• 7oil solution
• 6xchangeable molybdenum on the anion exchange sites
• 8rimary and secondary molybdenum minerals
• +rganic matter
Instead of being held onto the cation exchange caacity, molybdenum is held to soil articles with an anion
exchange caacity &including amorhous materials, iron oxides, acidic "aolin clays'. +rganic molybdenum
undergoes minerali)ation and immobili)ation.
BORON
Boron exists in the soil as:
• soil solution boron
• exchangeable boron on the anion exchange caacity sites
• rimary and secondary boron minerals
• Boron and organic matter comlexes
Boron is the only nonmetal micronutrient described in this section. *(B+( is most common form of boron in soils
that have a * between and ;. The exchangeable boron buffers changes in the boron levels of the soil solution.
+rganic matter sulies lant available boron. Boron should be carefully managed when alied to the soil since
the range between boron sufficiency and toxicity levels is very narrow.
Factors affecting micronutrient availability
IRON
• Soil pH : The availability of iron may be limited in soils with high *, esecially in arid, calcareous soils.
o 6xcessive liming can induce iron deficiencies.
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• Soil Moisture and Aeration: 8oorly aerated soils with excessive moisture in calcareous soil can
romote iron deficiencies.
o *owever, flooding of noncalcareous soils can imrove iron availability.
• Organic Matter : +rganic matter imroves iron availability due to chelation, which increases iron
solubility. -dditions of manure can increase chelation.
• Interactions with other nutrients: 6xcessive amounts of other micronutrients, articularly coer,
manganese, )inc and molybdenum, can decrease iron availability
MANGANESE
• Soil pH : 7oils with high * have limited manganese availability since manganese reciitates at high
*.
o +verliming soils can cause Mn deficiencies.
• Soil Moisture and Aeration: *igh soil moisture and oor aeration increases the availability of
manganese due to an increase in solubility.
• Organic Matter : Manganese availability increases with the addition of natural organic matter &i.e.
comost' due to favorable chelation which increases the level of exchangeable and solution
manganese.
• Climate: 5et conditions and warm temeratures increase manganese availability.
• Interactions with other nutrients: *igh amounts of coer, iron, and )inc may induce manganese
deficiency.
ZINC
• Soil pH : Zinc availability decreases as * increases.
o +verliming decreases Zn solubility.
• Zn adsorption: Though the relative amount of )inc on the cation exchange caacity is low, )inc is
attracted and held tightly to magnesite, dolomite and CaC+( minerals. -s a result, soils containing
these minerals can develo )inc deficiencies.
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• Organic Matter : 7oluble )inc chelates increase )inc availability.
• Climate: Cool, wet weather generally has a negative effect on )inc availability.
o Increasing soil temeratures increases )inc availability.
• Flooding : #looding generally decreases )inc availability.
o *owever, lowering the * of flooded soils may increase )inc availability.
• Interactions with other nutrients: Coer, iron, manganese, and hoshorus can interfere with )inc
uta"e.
COPPER
• Soil texture: Coer availability is lower in highly leached, coarse textured soils.
• Soil pH : Coer availability decreases as * increases, rimarily due to decreased solubility of coer
minerals.
• Organic matter : Coer forms very tight bonds with organic matter &more so than any other
micronutrient', which may reduce its availability in organic &eat and muc"' soils.
• Buried Cu : Coer may be occluded, or 3buried,4 within the structure of clay minerals and oxides.
+ccluded Cu is not available to lants.
• Interactions with other nutrients: Coer availability to lants may be reduced when )inc, iron, and0or
hoshorus contents are high in the soil solution.
MOLYBDENUM
• Soil pH : 9nli"e the other micronutrients, the availability of molybdenum increases with increasing *.
o -s a result, liming acidic soils increases molybdenum availability.
• Fe/Al oxides: Molybdenum is strongly held onto the surfaces of aluminum and iron oxides, which
reduces its availability.
• Interactions with other nutrients: Coer and manganese can reduce the uta"e of molybdenum by
lants. 8hoshate enhances molybdenum uta"e.
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• Soil moisture: 1ow levels of soil moisture reduce molybdenum availability.
BORON
• Soil pH : Boron availability decreases as * increases.
o 1iming can temorarily induce boron deficiencies, or lessen boron toxicities.
• Soil organic matter : +rganic matter increases boron availability.
• Soil texture: *ighly leached, coarse textured soils tend to have low boron availability.
• Plant actors: The range between boron sufficiency and boron toxicity is very narrow. Cro sensitivity to
boron varies, and it is imortant to become familiar with the boron sensitivity of your cro.
• Interactions with other nutrients: Cros are less sensitive to boron when there is amle amount of
calcium. This is because calcium acts to reduce boron availability. Boron may become deficient when
the Ca:B range is greater than
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)a+le %, Ma*or ele(ents- their sources and !unctions in +acterial cells,
Element% of dry
weightSource Function
Carbon 50
organic compounds
or CO2 Main constituent of cellular material
Oxygen 20
H2O, organic
compounds, CO2,
and O2
Constituent of cell material and cell
ater! O2 is electron acceptor in
aerobic respiration
"itrogen #$ "H%, "O%, organic
compounds, "2
Constituent of amino acids, nucleic
acids nucleotides, and coen&ymes
Hydrogen 'H2O, organic
compounds, H2
Main constituent of organic
compounds and cell ater
()osp)orus %inorganic
p)osp)ates *(O$+
Constituent of nucleic acids,
nucleotides, p)osp)olipids, (-,
teic)oic acids
-ulfur #
-O$, H2-, -o,
organic sulfurcompounds
Constituent of cysteine, met)ionine,
glutat)ione, several coen&ymes
(otassium # (otassium saltsMain cellular inorganic cation and
cofactor for certain en&ymes
Magnesium 0.5 Magnesium salts/norganic cellular cation, cofactor for
certain en&ymatic reactions
Calcium 0.5 Calcium salts
/norganic cellular cation, cofactor for
certain en&ymes and a component of
endospores
/ron 0.2 /ron salts
Component of cytoc)romes and
certain non)eme ironproteins and a
cofactor for some en&ymatic reactions
)race Ele(ents
Table < ignores the occurrence of trace elements in bacterial nutrition. )race ele(ents are metal ions reAuired by
certain cells in such small amounts that it is difficult to detect &measure' them, and it is not necessary to add them to
culture media as nutrients. Trace elements are reAuired in such small amounts that they are resent as contaminants
of the water or other media comonents. -s metal ions, the trace elements usually act as cofactors for essential
en)ymatic reactions in the cell. +ne organisms trace element may be anothers reAuired element and viceversa, but
the usual cations that Aualify as trace elements in bacterial nutrition are Mn, Co, Zn, Cu, and Mo.
Car+on and Ener$. Sources !or Bacterial Groth
In order to grow in nature or in the laboratory, a bacterium must have an energy source, a source of carbon and other
reAuired nutrients, and a ermissive range of hysical conditions such as +$ concentration, temerature, and *.
7ometimes bacteria are referred to as individuals or grous based on their atterns of growth under various chemical
&nutritional' or hysical conditions. #or examle, hototrohs are organisms that use light as an energy sourceD
anaerobes are organisms that grow without oxygenD thermohiles are organisms that grow at high temeratures.
-ll living organisms reAuire a source of energy. +rganisms that use radiant energy &light' are called #hototro#hs.
+rganisms that use &oxidi)e' an organic form of carbon are calledheterotro#hs or "che(o&heterotro#hs. +rganisms
that oxidi)e inorganic comounds are called lithotro#hs.
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The carbon reAuirements of organisms must be met by organic carbon &a chemical comound with a carbonhydrogen
bond' or by C+$. +rganisms that use organic carbon areheterotro#hs and organisms that use C+$ as a sole source of
carbon for growth are calledautotro#hs.
Thus, on the basis of carbon and energy sources for growth four maEor nutritional tyes of rocaryotes may be defined
&Table $'.
)a+le /, Ma*or nutritional t.#es o! #rocar.otes
Nutritional Type Energy SourceCarbon
SourceExamples
()otoautotrop)s ig)t CO2
Cyanobacteria, some
(urple and 1reen
acteria
()oto)eterotrop)s ig)tOrganic
compounds
-ome (urple and
1reen acteria
C)emoautotrop)s or
it)otrop)s*it)oautotrop)s+
/norganic
compounds, e.g.H2, "H%, "O2, H2-
CO23 fe acteria and
many 3rc)aea
C)emo)eterotrop)s or
Heterotrop)s
Organic
compounds
Organic
compounds
Most acteria, some
3rc)aea
-lmost all eucaryotes are either hotoautotrohic &e.g. lants and algae' or heterotrohic &e.g. animals, roto)oa, fungi'.1ithotrohy is uniAue to rocaryotes and hotoheterotrohy, common in the 8urle and 2reen Bacteria, occurs only in avery few eucaryotic algae. 8hototrohy has not been found in the -rchaea, excet for nonhotosynthetic lightdriven
-T8 synthesis in the extreme halohiles.
http://www.hindawi.com/journals/bmri/2013/597282/ journal fx mironutri!nthttp://"ai#bio.wordpr!ss.com/2009/01/31/nutrisi$miroba$s!buah$!s!nsi$dasar$untu$!hidupan$miroba/http://t!xtbooo#bact!riolo%&.n!t/nut%ro.html
http://www.hindawi.com/journals/bmri/2013/597282/http://zaifbio.wordpress.com/2009/01/31/nutrisi-mikroba-sebuah-esensi-dasar-untuk-kehidupan-mikroba/http://zaifbio.wordpress.com/2009/01/31/nutrisi-mikroba-sebuah-esensi-dasar-untuk-kehidupan-mikroba/http://textbookofbacteriology.net/nutgro.htmlhttp://zaifbio.wordpress.com/2009/01/31/nutrisi-mikroba-sebuah-esensi-dasar-untuk-kehidupan-mikroba/http://zaifbio.wordpress.com/2009/01/31/nutrisi-mikroba-sebuah-esensi-dasar-untuk-kehidupan-mikroba/http://textbookofbacteriology.net/nutgro.htmlhttp://www.hindawi.com/journals/bmri/2013/597282/