{"id":961,"date":"2026-06-11T07:43:50","date_gmt":"2026-06-11T07:43:50","guid":{"rendered":"https:\/\/rock-crusher-tractor.com\/?p=961"},"modified":"2026-06-11T07:43:50","modified_gmt":"2026-06-11T07:43:50","slug":"rock-crusher-blueberry-farm-acidic-soil-root-zone-guide","status":"publish","type":"post","link":"https:\/\/rock-crusher-tractor.com\/tr\/rock-crusher-blueberry-farm-acidic-soil-root-zone-guide\/","title":{"rendered":"Yaban Mersini \u00c7iftli\u011fi \u0130\u00e7in Kaya K\u0131r\u0131c\u0131 \u2014 Asidik Toprak K\u00f6k B\u00f6lgesi K\u0131lavuzu"},"content":{"rendered":"
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YABAN MERS\u0130N\u0130 \u00c7\u0130FTL\u0130\u011e\u0130 BA\u015eVURUSU<\/span><\/div>\n

Yaban Mersini \u00c7iftli\u011fi \u0130\u00e7in Kaya K\u0131r\u0131c\u0131 \u2014 Asidik Toprak K\u00f6k B\u00f6lgesi K\u0131lavuzu<\/h1>\n

Tek bir kire\u00e7 ta\u015f\u0131 par\u00e7as\u0131, yerel pH de\u011ferini 7,0'ye y\u00fckseltir; bu noktada hi\u00e7bir g\u00fcbre, \u00fczerindeki yaban mersini bitkisinin demir ihtiyac\u0131n\u0131 kar\u015f\u0131layamaz.<\/p>\n

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pH 4,5\u20135,5<\/div>\n
Gerekli toprak pH aral\u0131\u011f\u0131<\/div>\n<\/div>\n
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6-8 ya\u015f<\/div>\n
\u00dcretken baston \u00f6mr\u00fc<\/div>\n<\/div>\n
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1 \u00e7ak\u0131l ta\u015f\u0131<\/div>\n
Kire\u00e7ta\u015f\u0131 = yerel pH \u00f6ld\u00fcrme b\u00f6lgesi<\/div>\n<\/div>\n<\/div>\n

Yaban Mersini Yeti\u015ftirme Alan\u0131 Dan\u0131\u015fmanl\u0131\u011f\u0131<\/a><\/p>\n<\/div>\n<\/div>\n<\/div>\n

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Yaban mersini (Vaccinium corymbosum<\/em> Yaban mersini (ve ilgili t\u00fcrler), d\u00fcnyan\u0131n en h\u0131zl\u0131 b\u00fcy\u00fcyen meyve \u00fcr\u00fcn\u00fcd\u00fcr; k\u00fcresel \u00fcretim 2005'ten beri \u00fc\u00e7 kat\u0131na \u00e7\u0131km\u0131\u015ft\u0131r ve \u015eili, ABD, G\u00fcney Afrika, Peru ve \u0130spanya, taze ve i\u015flenmi\u015f pazar\u0131n b\u00fcy\u00fck bir k\u0131sm\u0131n\u0131 birlikte kar\u015f\u0131lamaktad\u0131r. Ba\u015fka hi\u00e7bir ticari \u00fcr\u00fcn\u00fcn gerektirmedi\u011fi dar bir pH aral\u0131\u011f\u0131nda (4,5-5,5) kas\u0131tl\u0131 olarak asitlendirilmi\u015f toprakta yeti\u015ftirilir ve ba\u015fka hi\u00e7bir b\u00fcy\u00fck meyve \u00fcr\u00fcn\u00fcn\u00fcn bu kadar tamamen ba\u011f\u0131ml\u0131 olmad\u0131\u011f\u0131 mikorizal besin eri\u015fim sistemini kullan\u0131r. Bu iki biyolojik ger\u00e7ek \u2013 a\u015f\u0131r\u0131 pH duyarl\u0131l\u0131\u011f\u0131 ve mikorizal ba\u011f\u0131ml\u0131l\u0131k \u2013 yaban mersini i\u00e7in bu E-serisi k\u0131lavuzundaki di\u011fer t\u00fcm \u00fcr\u00fcnlerden kategorik olarak farkl\u0131 bir \u00e7ekirdek y\u00f6netimi gereksinimi yarat\u0131r.<\/p>\n

Bu serideki \u00f6nceki her hasat i\u00e7in sorulan soru \u015fuydu: \u00c7ekirdek ne kadar b\u00fcy\u00fck, \u00e7ekirdek nerede ve ka\u00e7 tane \u00e7ekirdek var? Yaban mersini i\u00e7in ise soru \u015fu: Bu ne t\u00fcr bir ta\u015f?<\/em> Yaban mersini yata\u011f\u0131ndaki bir granit kaya par\u00e7as\u0131 fiziksel bir engeldir; rahats\u0131z edicidir, damlama sulama band\u0131na zarar verir, k\u00f6k geli\u015fimini engeller. Yaban mersini yata\u011f\u0131ndaki golf topu b\u00fcy\u00fckl\u00fc\u011f\u00fcndeki bir kire\u00e7 ta\u015f\u0131 \u00e7ak\u0131l\u0131 ise, yerel toprak pH'\u0131n\u0131 gerekli 4,8'den \u00fc\u00e7 y\u0131l i\u00e7inde 7,0'\u0131n \u00fczerine \u00e7\u0131karacak, demir ve manganezin bitki i\u00e7in kimyasal olarak kullan\u0131lamaz hale gelmesine neden olacak, \u00e7evresindeki erikoid mikorizal a\u011f\u0131 yok edecek ve besin yetersizli\u011finden dolay\u0131 4-5. y\u0131lda bitkinin \u00f6lmesine yol a\u00e7acak yava\u015f sal\u0131n\u0131ml\u0131 bir pH bombas\u0131d\u0131r; s\u00fcre\u00e7 ba\u015flad\u0131ktan sonra d\u00fczeltici bir tedavi mevcut de\u011fildir. Bu k\u0131lavuz \u015funlar\u0131 kapsar: yaban mersini \u00e7iftli\u011fi i\u00e7in kaya k\u0131r\u0131c\u0131<\/strong> Bu sorun, onu e\u015fsiz k\u0131lan kimyas\u0131, onu acil k\u0131lan biyolojisi ve her iki sorunun da ortaya \u00e7\u0131kt\u0131\u011f\u0131 pazarlar\u0131n jeolojisi arac\u0131l\u0131\u011f\u0131yla uygulanabilir.<\/p>\n

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Kire\u00e7ta\u015f\u0131 pH Mekanizmas\u0131 \u2014 Ta\u015f T\u00fcr\u00fc, Ta\u015f Miktar\u0131ndan Daha \u00d6nemlidir<\/h2>\n

\"THOR<\/p>\n

Kire\u00e7ta\u015f\u0131n\u0131n yaban mersini i\u00e7in neden benzersiz derecede tehlikeli oldu\u011funu a\u00e7\u0131klamak, topraktaki demir ve manganez bulunabilirli\u011finin \u00f6zel kimyas\u0131n\u0131 anlamay\u0131 gerektirir; bu iki besin maddesine yaban mersini pH 5,5'in \u00fczerinde eri\u015femez ve bunlar\u0131n eksikli\u011fi, dikkatsiz ta\u015f y\u00f6netimi sonucu bitki \u00f6l\u00fcm\u00fcne yol a\u00e7ar.<\/p>\n

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\u2460<\/span><\/p>\n
Asidik topraklarda kire\u00e7ta\u015f\u0131 \u00e7\u00f6z\u00fcnmesi \u2014 yava\u015f pH bombas\u0131.<\/strong> pH'\u0131 4,8 olan yaban mersini k\u00f6k b\u00f6lgesi topra\u011f\u0131na yerle\u015ftirilen bir kire\u00e7ta\u015f\u0131 par\u00e7as\u0131 (CaCO\u2083), k\u00f6k solunumu ve toprak mikrobiyal aktivitesiyle \u00fcretilen karbonik asit (H\u2082CO\u2083) kalsiyum karbonat y\u00fczeyine s\u00fcrekli olarak sald\u0131rd\u0131\u011f\u0131 i\u00e7in hemen \u00e7\u00f6z\u00fcnmeye ba\u015flar. \u00c7\u00f6z\u00fcnme reaksiyonu: CaCO\u2083 + H\u2082CO\u2083 \u2192 Ca\u00b2\u207a + 2HCO\u2083\u207b. Bu reaksiyon, toprak suyuna kalsiyum iyonlar\u0131 ve bikarbonat iyonlar\u0131 salar; bikarbonat, yerel toprak pH'\u0131n\u0131 y\u00fckselten birincil alkalile\u015ftirici ajand\u0131r. Tipik toprak asidi \u00e7\u00f6z\u00fcnme h\u0131zlar\u0131nda \u00e7\u00f6z\u00fcnen 5 cm \u00e7ap\u0131ndaki bir kire\u00e7ta\u015f\u0131 par\u00e7as\u0131, ta\u015f y\u00fczeyinin yakla\u015f\u0131k 8-12 cm yar\u0131\u00e7ap\u0131ndaki bir alanda 2-4 y\u0131l boyunca pH 6,5-7,2'lik bir b\u00f6lgeyi korumak i\u00e7in yeterli bikarbonat salar. Ta\u015f \u00e7\u00f6z\u00fcnmeye devam ettik\u00e7e bu b\u00f6lge geni\u015fler ve s\u00fcre\u00e7 kendi kendini devam ettirir \u00e7\u00fcnk\u00fc daha y\u00fcksek pH \u00e7\u00f6z\u00fcnmeyi yava\u015flat\u0131r ancak durdurmaz.<\/div>\n<\/div>\n
\u2461<\/span><\/p>\n
pH de\u011ferinin 5,5'in \u00fczerine \u00e7\u0131kmas\u0131, demir ve manganezin kullan\u0131lamamas\u0131na yol a\u00e7ar.<\/strong> Toprak demiri iki formda bulunur: Fe\u00b2\u207a (ferroz, \u00e7\u00f6z\u00fcn\u00fcr ve pH 5,5\u20136,0'\u0131n alt\u0131nda bitki taraf\u0131ndan kullan\u0131labilir) ve Fe\u00b3\u207a (ferrik, pH 5,5'in \u00fczerinde \u00e7\u00f6z\u00fcnmez). pH 6,5'te (kire\u00e7ta\u015f\u0131 \u00e7\u00f6z\u00fcnme b\u00f6lgesinin alt s\u0131n\u0131r\u0131) toprak \u00e7\u00f6zeltisindeki kullan\u0131labilir demir konsantrasyonu, pH 5,0'daki de\u011ferinin yakla\u015f\u0131k 1%'sine d\u00fc\u015fer. pH 7,0'de, inorganik toprak kaynaklar\u0131ndan kullan\u0131labilir demir neredeyse s\u0131f\u0131rd\u0131r. Yaban mersini, \u00e7o\u011fu meyve bitkisine k\u0131yasla son derece y\u00fcksek bir demir ihtiyac\u0131na sahiptir (demir, klorofil sentezi, fotosentezde elektron ta\u015f\u0131n\u0131m\u0131 ve k\u00f6kle ili\u015fkili bakteriler taraf\u0131ndan azot fiksasyonu i\u00e7in gereklidir). Manganez de ayn\u0131 pH-\u00e7\u00f6z\u00fcn\u00fcrl\u00fck modelini izler: kullan\u0131labilir Mn\u00b2\u207a, pH 5,5'in \u00fczerinde keskin bir \u015fekilde d\u00fc\u015fer ve pH 6,5'in \u00fczerinde s\u0131f\u0131ra yak\u0131nd\u0131r. Her iki eksiklik de ayn\u0131 erken belirtileri g\u00f6sterir: damarlar aras\u0131 kloroz (yaprak damarlar\u0131 ye\u015fil kal\u0131rken, damarlar aras\u0131ndaki doku sar\u0131-krem rengine d\u00f6ner). Bu nedenle, saha te\u015fhisinde bu iki eksiklik bazen kar\u0131\u015ft\u0131r\u0131l\u0131r.<\/div>\n<\/div>\n
\u2462<\/span><\/p>\n
Geri d\u00f6n\u00fc\u015f\u00fc olmayan bitki \u00e7\u00fcr\u00fcmesi \u2014 yerle\u015fmi\u015f kire\u00e7ta\u015f\u0131 b\u00f6lgeleri i\u00e7in d\u00fczeltici tedavi yok.<\/strong> Bir kere kire\u00e7ta\u015f\u0131 par\u00e7as\u0131 yaban mersini tarlas\u0131nda yerel toprak pH'\u0131n\u0131 6,5'in \u00fczerine \u00e7\u0131kard\u0131\u011f\u0131nda, tedavi se\u00e7enekleri s\u0131n\u0131rl\u0131d\u0131r ve b\u00fcy\u00fck \u00f6l\u00e7\u00fcde etkisizdir. Y\u00fczeyden k\u00fck\u00fcrt uygulamas\u0131 topra\u011f\u0131n \u00fcst 10 cm'sini asitle\u015ftirebilir ancak \u00e7\u00f6z\u00fcnm\u00fc\u015f kalsiyumun ta\u015f par\u00e7alar\u0131n\u0131n etraf\u0131nda birikti\u011fi 20-30 cm derinli\u011fe etkili bir \u015fekilde n\u00fcfuz edemez. \u015eelatl\u0131 demir yaprak spreyleri ge\u00e7ici bir ye\u015fillenme sa\u011flar ancak altta yatan toprak kimyas\u0131 sorununu \u00e7\u00f6zemez. 2-3 y\u0131l \u00e7\u00f6z\u00fcnme sonras\u0131nda kire\u00e7ta\u015f\u0131 par\u00e7as\u0131n\u0131 \u00e7\u0131karmak, etkilenen toprak hacminin (tipik olarak par\u00e7a ba\u015f\u0131na 20-40 litre de\u011fi\u015fmi\u015f toprak) kaz\u0131lmas\u0131n\u0131 ve yerine asitlendirilmi\u015f yeti\u015ftirme ortam\u0131 konulmas\u0131n\u0131 gerektirir. Yerle\u015fik bir yaban mersini tarlas\u0131nda bu kaz\u0131, ta\u00e7tan her y\u00f6ne 30-60 cm uzanan s\u0131\u011f k\u00f6k a\u011f\u0131n\u0131 zedeler. Pratik sonu\u00e7: 15 y\u0131ll\u0131k bir tarlan\u0131n 3. y\u0131l\u0131nda ke\u015ffedilen bir yaban mersini yata\u011f\u0131ndaki kire\u00e7ta\u015f\u0131 kirlili\u011fi, kalan 12 y\u0131l boyunca bu b\u00f6lgelerde kal\u0131c\u0131 \u00fcretim kayb\u0131 anlam\u0131na gelir.<\/div>\n<\/div>\n
\u2463<\/span><\/p>\n
THOR ezme + CT-2100 toplama: tek \u00f6nlem.<\/strong> Yaban mersini yeti\u015ftirilen alanlardaki kire\u00e7ta\u015f\u0131 i\u00e7in tek etkili y\u00f6netim y\u00f6ntemi, ekim \u00f6ncesi temizlemedir. THOR kaya k\u0131r\u0131c\u0131, kire\u00e7ta\u015f\u0131n\u0131 <3\u20135 cm'lik par\u00e7alara ay\u0131r\u0131r; CT-2100 ta\u015f toplay\u0131c\u0131<\/a> Par\u00e7alar\u0131 kal\u0131c\u0131 olarak ortadan kald\u0131r\u0131r. Toprak sondalamas\u0131yla kar\u0131\u015f\u0131k ta\u015f t\u00fcrlerinin (kire\u00e7 ta\u015f\u0131 ve granit bir arada bulunur) tespit edildi\u011fi alanlarda, temizleme \u015fartnamesi t\u00fcm kire\u00e7 ta\u015f\u0131 par\u00e7alar\u0131n\u0131n tamamen ortadan kald\u0131r\u0131lmas\u0131n\u0131 sa\u011flamal\u0131d\u0131r; k\u00fc\u00e7\u00fck bir kal\u0131nt\u0131 kire\u00e7 ta\u015f\u0131 pop\u00fclasyonu bile yukar\u0131da a\u00e7\u0131klanan pH y\u00fckselme b\u00f6lgelerini olu\u015fturacakt\u0131r. 30-35 cm'ye kadar THOR temizli\u011fi ve ard\u0131ndan CT-2100 toplama i\u015flemi, temizlik sonras\u0131 pH sondas\u0131 ara\u015ft\u0131rmas\u0131yla do\u011fruland\u0131ktan sonra, kire\u00e7 ta\u015f\u0131 i\u00e7eren ana materyale sahip herhangi bir alanda yaban mersini i\u00e7in standart ekim \u00f6ncesi protokold\u00fcr.<\/div>\n<\/div>\n<\/div>\n

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Toprak pH'\u0131 ve Demir\/Mangan Bulunabilirli\u011fi Aras\u0131ndaki \u0130li\u015fki \u2014 Yaban Mersini \u0130\u00e7in Kritik D\u00f6nem<\/p>\n

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pH 3<\/div>\n
pH 4<\/div>\n
pH 4,5\u20135,5 \u2605<\/div>\n
pH 5.5<\/div>\n
pH 6.0<\/div>\n
pH 6,5<\/div>\n
pH 7.0+<\/div>\n
pH 8<\/div>\n<\/div>\n
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Fe \u2713\u2713\u2713<\/div>\n
Fe \u2713\u2713\u2713<\/div>\n
Fe \u2713\u2713\u2713 OPT\u0130MAL<\/div>\n
Fe \u2713\u2713<\/div>\n
Fe \u2713<\/div>\n
Fe \u22480<\/div>\n
Fe = 0 \u2620<\/div>\n
Fe = 0<\/div>\n<\/div>\n
\u2605 Yaban mersini 4,5\u20135,5 pH aral\u0131\u011f\u0131n\u0131 gerektirir.<\/strong> Bir kire\u00e7ta\u015f\u0131 \u00e7ak\u0131l\u0131, 10-12 cm yar\u0131\u00e7ap i\u00e7inde pH 6,5-7,0 aral\u0131\u011f\u0131nda bir mikro b\u00f6lge olu\u015fturur.
\npH 6,5'te: demir kullan\u0131labilirli\u011fi optimumun ~'i kadard\u0131r. pH 7,0'te: demir kullan\u0131labilirli\u011fi yakla\u015f\u0131k %0'd\u0131r. Sonu\u00e7: kloroz \u2192 \u00f6l\u00fcm.<\/div>\n<\/div>\n<\/div>\n

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Ta\u015f T\u00fcr\u00fc Risk Matrisi \u2014 Granit ve Kire\u00e7ta\u015f\u0131 Neden Ayn\u0131 Sorun De\u011fil?<\/h2>\n

Bu E-16 makalesinin temel fikri \u2013 yaban mersini i\u00e7in ta\u015f t\u00fcr\u00fcn\u00fcn ta\u015f miktar\u0131ndan daha \u00f6nemli oldu\u011fu \u2013 saha de\u011ferlendirmesi ve makine spesifikasyonu a\u00e7\u0131s\u0131ndan pratik sonu\u00e7lar do\u011furmaktad\u0131r. 20-30 cm derinlikte y\u00fcksek granit ta\u015f yo\u011funlu\u011funa sahip bir alan, standart THOR temizli\u011fi ile \u00e7\u00f6z\u00fclebilen fiziksel bir k\u00f6k k\u0131s\u0131tlama problemidir. 20-30 cm derinlikte d\u00fc\u015f\u00fck kire\u00e7 ta\u015f\u0131 yo\u011funlu\u011funa sahip bir alan ise, her bir kire\u00e7 ta\u015f\u0131 par\u00e7as\u0131n\u0131n tamamen kald\u0131r\u0131lmas\u0131n\u0131 gerektiren kimyasal bir toprak tahribat\u0131 problemidir. Saha haz\u0131rl\u0131\u011f\u0131ndan \u00f6nce de\u011ferlendirme metodolojisi bu iki senaryoyu birbirinden ay\u0131rmal\u0131d\u0131r.<\/p>\n

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Yaban Mersini \u0130\u00e7in Ta\u015f Tipi Risk Matrisi \u2014 Kimyasal ve Fiziksel Hasar Mekanizmas\u0131<\/caption>\n
Ta\u015f T\u00fcr\u00fc<\/th>\nMohs<\/th>\nCa\u00b2\u207a sal\u0131n\u0131m\u0131<\/th>\npH y\u00fckselmesi riski<\/th>\nTehlike seviyesi<\/th>\nYaban mersini sonucu<\/th>\n<\/tr>\n<\/thead>\n
Kire\u00e7ta\u015f\u0131 (CaCO\u2083)<\/td>\n3\u20134<\/td>\nY\u00dcKSEK<\/td>\npH 6,5\u20137,5 b\u00f6lgesi<\/td>\n\u2620\u2620\u2620 \u00d6L\u00dcMC\u00dcL<\/td>\nDemir\/Mangan yetersizli\u011fi \u2192 kloroz \u2192 bitki ba\u015f\u0131na 4-5 y\u0131l i\u00e7inde \u00f6l\u00fcm<\/td>\n<\/tr>\n
Tebe\u015fir (yumu\u015fak kire\u00e7 ta\u015f\u0131)<\/td>\n1\u20132<\/td>\n\u00c7OK Y\u00dcKSEK<\/td>\npH 7.0\u20138.0 b\u00f6lgesi (daha h\u0131zl\u0131)<\/td>\n\u2620\u2620\u2620\u2620 DAHA \u00d6L\u00dcMC\u00dcL<\/td>\nDaha yumu\u015fak tebe\u015fir daha h\u0131zl\u0131 \u00e7\u00f6z\u00fcn\u00fcr \u2192 pH y\u00fckselmesi 2-4. y\u0131llar yerine 1-2. y\u0131llarda g\u00f6r\u00fcl\u00fcr.<\/td>\n<\/tr>\n
Dolomit (CaMg(CO\u2083)\u2082)<\/td>\n3\u20134<\/td>\nORTA-Y\u00dcKSEK<\/td>\npH 6,5\u20137,5 b\u00f6lgesi (daha yava\u015f)<\/td>\n\u2620\u2620 C\u0130DD\u0130<\/td>\nKire\u00e7ta\u015f\u0131na g\u00f6re daha yava\u015f \u00e7\u00f6z\u00fcn\u00fcr ama sonu\u00e7 ayn\u0131d\u0131r. Kald\u0131r\u0131lmas\u0131 gerekir.<\/td>\n<\/tr>\n
Granit \/ granodiyorit<\/td>\n6\u20137<\/td>\n\u00c7OK D\u00dc\u015e\u00dcK<\/td>\n\u00d6nemsiz<\/td>\n\u26a0 Sadece fiziksel olarak<\/td>\nSadece fiziksel k\u00f6k t\u0131kan\u0131kl\u0131\u011f\u0131 ve damlama band\u0131 hasar\u0131 s\u00f6z konusu; pH \u00fczerinde etkisi yok. Standart temizleme.<\/td>\n<\/tr>\n
Kuvarsit \/ \u00e7akmakta\u015f\u0131<\/td>\n7\u20138<\/td>\nSIFIR<\/td>\nHi\u00e7biri<\/td>\n\u26a0 Sadece fiziksel olarak<\/td>\nAsidik topraklarda kimyasal olarak inerttir. Sadece fiziksel k\u00f6k k\u0131s\u0131tlamas\u0131na neden olur. Damlama sulama band\u0131 ve k\u00f6k \u00f6rt\u00fcs\u00fcne zarar verir.<\/td>\n<\/tr>\n
Volkanik bazalt (vezik\u00fcler)<\/td>\n5\u20136<\/td>\nD\u00dc\u015e\u00dcK<\/td>\nHafif (yerel olarak pH 5.0\u20135.5)<\/td>\n\u26a0 D\u00fc\u015f\u00fck kimyasal i\u00e7erikli<\/td>\nBazalt matrisinde bir miktar kalsiyum bulunur, ancak genel olarak Pasifik Kuzeybat\u0131's\u0131ndaki volkanik b\u00f6lgelerde yaban mersini pH gereksinimleriyle uyumludur.<\/td>\n<\/tr>\n<\/tbody>\n<\/table>\n<\/div>\n

<\/p>\n

Ericoid Mikoriza \u2014 Ta\u015f\u0131n Yok Etti\u011fi G\u00f6r\u00fcnmez Besin Sistemi<\/h2>\n

\"CT-2100<\/p>\n

Yaban mersininin al\u0131\u015f\u0131lmad\u0131k beslenme gereksinimleri \u2014 \u00e7o\u011fu bitkinin hayatta kalamad\u0131\u011f\u0131 a\u015f\u0131r\u0131 asidik topraklarda yeti\u015febilme yetene\u011fi, geleneksel azot sabitleyici bakteriler olmadan organik asidik topraklarda azota eri\u015febilme kapasitesi \u2014 Ericaceae bitki ailesine \u00f6zg\u00fc bir mikorizal ortakl\u0131\u011fa ba\u011fl\u0131d\u0131r. Bu ortakl\u0131\u011f\u0131 anlamak, yaban mersini i\u00e7in ta\u015f temizli\u011finin neden sadece fiziksel bir k\u00f6k b\u00f6lgesi haz\u0131rl\u0131\u011f\u0131ndan daha fazlas\u0131 oldu\u011funu ve B\u00f6l\u00fcm 1'de a\u00e7\u0131klanan kire\u00e7ta\u015f\u0131 pH sonu\u00e7lar\u0131n\u0131n, bitki \u00f6rt\u00fcs\u00fcnde g\u00f6r\u00fcn\u00fcr belirtiler ortaya \u00e7\u0131kmadan \u00f6nce yaban mersini bitkilerini neden etkiledi\u011fini a\u00e7\u0131klar.<\/p>\n

\n
Ericoid mikorizan\u0131n yapt\u0131\u011f\u0131 \u015fey<\/strong><\/p>\n

Meyve a\u011fa\u00e7lar\u0131n\u0131n (elma, turun\u00e7giller, ceviz) \u00e7o\u011funun kulland\u0131\u011f\u0131 arbuskuler mikorizan\u0131n aksine, yaban mersini farkl\u0131 bir mikoriza kullan\u0131r. erikoid mikoriza<\/em> \u2014 son derece asidik organik topraklara \u00f6zelle\u015fmi\u015f, kendine \u00f6zg\u00fc bir mantar ortakl\u0131\u011f\u0131. Ericoid mantarlar yaban mersini k\u0131l k\u00f6klerine n\u00fcfuz eder ve k\u00f6k y\u00fczeyinin \u00e7ok \u00f6tesine, \u00e7evredeki topra\u011fa uzanarak, bitki k\u00f6klerinin tek ba\u015f\u0131na eri\u015femedi\u011fi formlardaki organik maddeden (amino asitler, proteinler) azot al\u0131r. Ayr\u0131ca asidik topraktaki organik molek\u00fcllere ba\u011fl\u0131 fosfora da eri\u015firler; bu formlar\u0131 geleneksel arbuskuler mikorizal mantarlar kullanamaz. pH 4,5-5,5 olan asidik topraklarda, ericoid mikoriza yaban mersininin azot al\u0131m\u0131n\u0131n -60%'sini ve fosfor al\u0131m\u0131n\u0131n -70%'sini sa\u011flar; ba\u015fka hi\u00e7bir da\u011f\u0131t\u0131m mekanizmas\u0131 bunun eksikli\u011fini telafi edemez.<\/p>\n<\/div>\n

Ta\u015f, erikoid mikorizay\u0131 nas\u0131l yok eder?<\/strong><\/p>\n

Ericoid mikorizal mantarlar zorunlu asidofillerdir; pH 6.0'\u0131n \u00fczerinde i\u015flev g\u00f6remezler ve pH 6.5'in \u00fczerinde h\u0131zla \u00f6l\u00fcrler. Yaban mersini k\u00f6k yata\u011f\u0131ndaki kire\u00e7ta\u015f\u0131 \u00e7\u00f6z\u00fcnme b\u00f6lgesi (pH 6.5\u20137.5), bitki k\u00f6kleri i\u00e7in sadece bir pH sorunu de\u011fildir: ayn\u0131 zamanda k\u00f6klerin ba\u011fl\u0131 oldu\u011fu erikoid mikorizal a\u011f i\u00e7in de \u00f6l\u00fcmc\u00fcl bir b\u00f6lgedir. Kire\u00e7ta\u015f\u0131ndan etkilenen topraktan uzanan mantar hifleri, pH y\u00fckseldik\u00e7e \u00f6l\u00fcr ve bitki herhangi bir g\u00f6r\u00fcn\u00fcr belirti g\u00f6stermeden \u00f6nce mikorizal ba\u011flant\u0131y\u0131 kopar\u0131r. Bitki, pH y\u00fckselmesinden kaynaklanan demir ve manganez eksikli\u011fi kloroz olarak g\u00f6r\u00fcn\u00fcr hale gelmeden aylar \u00f6nce azot ve fosfor eksikli\u011fi ya\u015famaya ba\u015flar. Kire\u00e7ta\u015f\u0131 par\u00e7alar\u0131 i\u00e7ermeyen, ta\u015ftan temizlenmi\u015f yaban mersini yataklar\u0131, ekimin 15-20 y\u0131ll\u0131k verimli \u00f6mr\u00fc boyunca s\u00fcrekli erikoid mikorizal a\u011f b\u00fct\u00fcnl\u00fc\u011f\u00fcn\u00fc korur.<\/p>\n<\/div>\n

Ta\u015flar\u0131n nem d\u00fczenini bozmas\u0131 mikorizay\u0131 da etkiler.<\/strong><\/p>\n

Yaban mersini k\u00f6k \u00f6rt\u00fcs\u00fcndeki kire\u00e7siz ta\u015flar (granit, kuvarsit) bile nem heterojenli\u011fi yoluyla erikoid mikorizal fonksiyonunu etkiler; bu, E-15 cevizindeki juglon i\u00e7in a\u00e7\u0131klanan mekanizmayla ayn\u0131d\u0131r. Ericoid mantarlar, hif a\u011flar\u0131n\u0131 korumak i\u00e7in s\u00fcrekli nemli (ancak suyla doymu\u015f olmayan) ko\u015fullara ihtiya\u00e7 duyar. K\u00f6k b\u00f6lgesindeki ta\u015flar, tutars\u0131z nem b\u00f6lgeleri olu\u015fturur; ta\u015flar\u0131n hemen \u00fcst\u00fcnde ve biti\u015fi\u011finde daha kuru, yama\u00e7 a\u015fa\u011f\u0131s\u0131nda daha nemli. Bu nem dalgalanmalar\u0131, pH etkilerinin yoklu\u011funda bile mikorizal a\u011f\u0131n baz\u0131 k\u0131s\u0131mlar\u0131n\u0131 periyodik olarak kurutarak a\u011f s\u00fcreklili\u011fini azalt\u0131r. Drenaj homojenli\u011fi iyile\u015ftirilmi\u015f ta\u015ftan ar\u0131nd\u0131r\u0131lm\u0131\u015f toprak, ta\u015fl\u0131 topra\u011fa g\u00f6re daha tutarl\u0131 mikorizal a\u011f nemi sa\u011flar; bu, sa\u011flad\u0131\u011f\u0131 pH korumas\u0131n\u0131n \u00f6tesinde ta\u015f temizlemenin ikincil bir faydas\u0131d\u0131r.<\/p>\n<\/div>\n<\/div>\n

<\/p>\n

Yaban Mersini K\u00f6k Yap\u0131s\u0131 \u2014 S\u0131\u011f Lifli \u00d6rt\u00fc ve \u00c7ubuk D\u00f6ng\u00fcs\u00fc<\/h2>\n

Yaban mersini k\u00f6k yap\u0131s\u0131, ticari meyve bitkileri aras\u0131nda en s\u0131\u011f olanlardan biridir; ku\u015fkonmaz, turun\u00e7giller veya f\u0131nd\u0131ktan \u00f6nemli \u00f6l\u00e7\u00fcde daha s\u0131\u011fd\u0131r ve asma besleyici k\u00f6klerinin \u00fcst aral\u0131\u011f\u0131yla kar\u015f\u0131la\u015ft\u0131r\u0131labilir. Bu s\u0131\u011fl\u0131k, yaban mersinini hem y\u00fczey ta\u015flar\u0131na (k\u00f6k tabakas\u0131na fiziksel hasar) hem de 15-35 cm b\u00f6lgesindeki kire\u00e7 ta\u015f\u0131na (birincil besleyici k\u00f6k derinli\u011finde pH y\u00fckselmesi) kar\u015f\u0131 \u00f6zellikle savunmas\u0131z hale getirir.<\/p>\n

\n\n\n\n\n\n\n\n
Yaban Mersini \u00c7e\u015fitleri \u2014 K\u00f6k Derinli\u011fi, Temizleme \u00d6zellikleri ve Ba\u015fl\u0131ca \u00dcretim B\u00f6lgesi<\/caption>\n
Tip<\/th>\nT\u00fcrler<\/th>\nK\u00f6k Derinli\u011fi<\/th>\nTemizleme Derinli\u011fi<\/th>\nBirincil B\u00f6lgeler<\/th>\nTa\u015f hassasiyeti<\/th>\n<\/tr>\n<\/thead>\n
Kuzey y\u00fcksek \u00e7al\u0131l\u0131klar\u0131<\/td>\nV. corymbosum<\/td>\n15\u201335 cm (lifli paspas)<\/td>\n28\u201338 cm<\/td>\nMichigan, Washington, Oregon, Britanya Kolombiyas\u0131, Kanada, \u015eili, G\u00fcney Afrika<\/td>\nEn y\u00fcksek - en s\u0131\u011f k\u00f6kler kire\u00e7ta\u015f\u0131na en \u00e7ok maruz kal\u0131r pH b\u00f6lgesi<\/td>\n<\/tr>\n
G\u00fcney y\u00fcksek \u00e7al\u0131l\u0131klar\u0131<\/td>\nV. corymbosum hibriti<\/td>\n20\u201340 cm<\/td>\n32\u201342 cm<\/td>\n\u0130spanya Huelva, Fas, Peru, Florida<\/td>\nY\u00fcksek \u2014 biraz daha derinde ama daha kire\u00e7li Akdeniz topraklar\u0131nda yeti\u015fir<\/td>\n<\/tr>\n
Tav\u015fan g\u00f6z\u00fc<\/td>\nV. virgatum<\/td>\n25\u201350 cm<\/td>\n38\u201352 cm<\/td>\nG\u00fcrcistan\/ABD'nin G\u00fcneydo\u011fusu, Avustralya, Yeni Zelanda, Arjantin<\/td>\nOrta d\u00fczeyde \u2014 daha derin k\u00f6kler y\u00fczeydeki kire\u00e7ta\u015f\u0131 \u00e7\u00f6z\u00fcnme b\u00f6lgesine daha az maruz kal\u0131r.<\/td>\n<\/tr>\n<\/tbody>\n<\/table>\n<\/div>\n
\u015eeker kam\u0131\u015f\u0131 yenileme d\u00f6ng\u00fcs\u00fc ve ta\u015f olu\u015fumu y\u00f6netimi:<\/strong> Y\u00fcksek \u00e7al\u0131 yaban mersini, \u00e7ok g\u00f6vdeli bir \u00e7al\u0131 olarak y\u00f6netilir; bitki ba\u015f\u0131na 8-12 verimli g\u00f6vde bulunur ve her biri 6-8 y\u0131l boyunca verimli olduktan sonra zay\u0131flar ve ta\u00e7tan yeni g\u00f6vdelerle de\u011fi\u015ftirilmek \u00fczere budan\u0131r. Bu g\u00f6vde devir d\u00f6ng\u00fcs\u00fc, yeni g\u00f6vde k\u00f6klerinin, dikimin 15-20 y\u0131ll\u0131k verimli \u00f6mr\u00fc boyunca s\u00fcrekli olarak biti\u015fik topra\u011fa do\u011fru geni\u015fledi\u011fi anlam\u0131na gelir. \u0130lk temizleme s\u0131ras\u0131nda g\u00f6zden ka\u00e7an herhangi bir kire\u00e7 ta\u015f\u0131 par\u00e7as\u0131, geni\u015fleyen k\u00f6k tabakas\u0131 par\u00e7aya ula\u015ft\u0131\u011f\u0131nda, dikimden 2-4 y\u0131l sonra yeni g\u00f6vde k\u00f6kleri taraf\u0131ndan kar\u015f\u0131lanacakt\u0131r. Y\u0131ll\u0131k ilkbahar bak\u0131m temizli\u011fi (g\u00f6vde k\u00f6k geni\u015flemesinin en fazla oldu\u011fu s\u0131ra aras\u0131 b\u00f6lgelerde 12-16 cm'de THOR 2.4), don kabarmas\u0131yla ta\u015f\u0131nan ta\u015f\u0131 geni\u015fleyen k\u00f6k \u00f6n\u00fcnden uzakla\u015ft\u0131r\u0131r ve g\u00f6r\u00fcn\u00fcr bitki semptomlar\u0131na neden olmadan \u00f6nce geli\u015fmekte olan kire\u00e7 ta\u015f\u0131 \u00e7\u00f6z\u00fcnme b\u00f6lgelerini belirlemek i\u00e7in pH probu ara\u015ft\u0131rmas\u0131 yapma f\u0131rsat\u0131 sa\u011flar.<\/div>\n

<\/p>\n

K\u00fcresel Yaban Mersini Pazarlar\u0131 \u2014 Kire\u00e7ta\u015f\u0131 ve Granitin Asidik Toprakla Bir Arada Bulundu\u011fu Yer<\/h2>\n
\n
\n
\ud83c\uddfa\ud83c\uddf8 Pasifik Kuzeybat\u0131s\u0131 \u2014 Washington, Oregon, Michigan<\/span>
\nD\u00fcnyan\u0131n en b\u00fcy\u00fck y\u00fcksek \u00e7al\u0131 hacmi<\/span><\/div>\n
Washington Eyaleti ve Oregon'daki Willamette Vadisi, yaban mersini \u00e7ekirde\u011fi y\u00f6netiminin paradoksunu temsil eder: do\u011fal olarak asidik volkanik ve buzul topraklar\u0131 (pH 4,5\u20135,5) yaban mersini i\u00e7in idealdir, ancak bu b\u00f6lgelerin alt\u0131nda yatan buzul tortusu, Pleistosen buzulla\u015fmas\u0131 s\u0131ras\u0131nda Kanada Kalkan\u0131'ndan ta\u015f\u0131nan de\u011fi\u015fken kire\u00e7ta\u015f\u0131 ve dolomit par\u00e7alar\u0131 i\u00e7erir. Kritik ayr\u0131m \u015fudur: B\u00f6lgenin do\u011fal volkanik topra\u011f\u0131 yaban mersini yeti\u015ftirmek i\u00e7in g\u00fcvenlidir.<\/strong> \u2014 asidik, silisli ve mikorizal olarak aktiftir. Buzul tortusu bile\u015feni tehlikelidir.<\/strong> \u2014 Uzak karbonat olu\u015fumlar\u0131ndan gelen kire\u00e7ta\u015f\u0131 ve dolomit \u00e7ak\u0131llar\u0131 i\u00e7erir. Puyallup Vadisi (Washington) ve Willamette Vadisi kenarlar\u0131ndaki yeni yaban mersini alanlar\u0131nda, buzul tortusu derinli\u011fini ve ta\u015f karbonat i\u00e7eri\u011fini belirlemek i\u00e7in toprak sondas\u0131, standart \u00f6n temizleme protokol\u00fcd\u00fcr. Tortu tabakas\u0131nda 15-35 cm'de >5% kire\u00e7ta\u015f\u0131\/dolomit par\u00e7alar\u0131 bulunan alanlarda, ta\u015f yo\u011funlu\u011funa bak\u0131lmaks\u0131z\u0131n ta\u015f\u0131n tamamen temizlenmesi gerekir. Michigan'\u0131n buzul manzaras\u0131 (g\u00fcneybat\u0131 Michigan - d\u00fcnyan\u0131n \u00fc\u00e7\u00fcnc\u00fc b\u00fcy\u00fck yaban mersini \u00fcreten eyaleti), di\u011fer tar\u0131msal kullan\u0131mlardan d\u00f6n\u00fc\u015ft\u00fcr\u00fclen alanlarda benzer buzul tortusu kire\u00e7ta\u015f\u0131 kirlili\u011fini g\u00f6stermektedir \u2014 standart temizleme i\u00e7in 25-32 cm'de THOR 2.4; temizleme sonras\u0131 pH ara\u015ft\u0131rmas\u0131 zorunludur.<\/div>\n<\/div>\n
\n
\ud83c\udde8\ud83c\uddf1 \u015eili \u2014 d\u00fcnyan\u0131n en b\u00fcy\u00fck yaban mersini ihracat\u00e7\u0131s\u0131<\/span>
\nSezon d\u0131\u015f\u0131 AB\/ABD arz\u0131<\/span><\/div>\n
\u015eili'nin yaban mersini \u00fcretimi, do\u011fal olarak asidik andisol topraklar (pH 4,5\u20135,8) \u00fcreten volkanik And Da\u011flar\u0131 eteklerindeki Los Lagos, Araucan\u00eda ve B\u00edo B\u00edo b\u00f6lgelerinde yo\u011funla\u015fm\u0131\u015ft\u0131r; bu topraklar y\u00fcksek \u00e7al\u0131 yaban mersini i\u00e7in idealdir. \u015eili yaban mersini \u00fcretimindeki en b\u00fcy\u00fck zorluk, \u00e7ekirdek y\u00f6netimidir. al\u00fcvyal kire\u00e7ta\u015f\u0131 kirlenmesi<\/strong> Orta And kire\u00e7ta\u015f\u0131 ku\u015fa\u011f\u0131n\u0131 drene eden nehirlerden: Maule, B\u00edo B\u00edo ve Caut\u00edn nehirleri, And s\u0131rada\u011flar\u0131ndaki Mezozoik kire\u00e7ta\u015f\u0131 olu\u015fumlar\u0131ndan kire\u00e7li \u00e7ak\u0131l ta\u015f\u0131yarak \u015eili yaban mersini yay\u0131l\u0131m\u0131n\u0131n en aktif oldu\u011fu al\u00fcvyal yelpazelere b\u0131rak\u0131r. Al\u00fcvyal yelpaze alanlar\u0131nda, do\u011fal volkanik asitli toprak, 15-40 cm derinlikte kire\u00e7li nehir \u00e7ak\u0131llar\u0131yla kirlenir. Ta\u015f y\u00f6netimi y\u00fck\u00fcml\u00fcl\u00fc\u011f\u00fc, Pasifik Kuzeybat\u0131 buzul tortusuyla ayn\u0131d\u0131r - sadece genel ta\u015f yo\u011funlu\u011funu azaltmak de\u011fil, t\u00fcm kire\u00e7li par\u00e7alar\u0131 \u00e7\u0131karmak gerekir. THOR 2.4 (180 HP), And kire\u00e7ta\u015f\u0131n\u0131 (Mohs 3-4) 2,0 km\/sa h\u0131zla i\u015fler; CT-2100 toplama; temizleme sonras\u0131 pH ara\u015ft\u0131rmas\u0131, 3 cm yar\u0131\u00e7ap \u00fczerindeki tespit edilen kal\u0131nt\u0131 karbonat\u0131n s\u0131f\u0131r oldu\u011funu do\u011frular. B\u00fcy\u00fck \u015eili yaban mersini geli\u015ftirmeleri (15+ ha) bu y\u00f6ntemi kullanmaktad\u0131r. BlackBird kaya t\u0131rm\u0131\u011f\u0131<\/a> Mekanik hasattan \u00f6nce y\u00fczey kontrol\u00fc \u2014 \u015eili y\u00fcksek \u00e7al\u0131l\u0131k elmalar\u0131n\u0131n hasad\u0131 a\u011f\u0131rl\u0131kl\u0131 olarak makineyle yap\u0131l\u0131r ve meyvelerin y\u00fczeyindeki ta\u015f kirlili\u011fi, AB taze \u00fcr\u00fcn pazar\u0131 i\u00e7in ba\u015fl\u0131ca kalite endi\u015felerinden biridir.<\/div>\n<\/div>\n
\n
\ud83c\uddea\ud83c\uddf8 \u0130spanya \u2014 Huelva, Avrupa'n\u0131n yaban mersini merkezi<\/span>
\nAB erken sezon premium pazar\u0131<\/span><\/div>\n
Huelva'n\u0131n AB'de erken sezon taze yaban mersini (Aral\u0131k-Mart) pazar\u0131ndaki hakimiyeti, Do\u00f1ana hinterland\u0131n\u0131n kumlu asidik topraklar\u0131na dayanmaktad\u0131r; bu topraklar do\u011fal olarak d\u00fc\u015f\u00fck ta\u015f i\u00e7eri\u011fine, 4,5-5,5 pH de\u011ferine ve erikoid mikorizal aktiviteye sahiptir. Huelva'daki ta\u015f y\u00f6netimi zorlu\u011fu ise \u015fudur: esas olarak yer alt\u0131 ta\u015f\u0131 de\u011fil<\/strong> (kumlu profillerin ta\u015f yo\u011funlu\u011fu d\u00fc\u015f\u00fckt\u00fcr) ancak iki ilgili fakt\u00f6r s\u00f6z konusudur. Birincisi: sulama suyu alkalili\u011fi<\/strong> \u2014 Huelva'n\u0131n damlama sulama sistemi, yukar\u0131 havzadaki kire\u00e7ta\u015f\u0131 olu\u015fumlar\u0131ndan \u00e7\u00f6z\u00fcnm\u00fc\u015f kalsiyum ta\u015f\u0131yan Odiel ve Tinto nehirlerinden su \u00e7ekmektedir. Y\u0131llarca pH 7.0\u20137.5 su ile damlama sulama yap\u0131ld\u0131\u011f\u0131nda, sulama b\u00f6lgesinde (tipik olarak damlama u\u00e7lar\u0131n\u0131n etraf\u0131nda 10\u201330 cm) biriken kalsiyum karbonat, ba\u015flang\u0131\u00e7ta asidik, ta\u015fs\u0131z topraklarda bile, fiziksel kire\u00e7ta\u015f\u0131 par\u00e7alar\u0131yla ayn\u0131 pH y\u00fckselme b\u00f6lgelerini olu\u015fturmaya ba\u015flar. Burada ta\u015f temizleme, \u00f6nceden pH tampon y\u00f6netimi ve sulama suyunun asitle\u015ftirilmesinden daha az \u00f6nemlidir. \u0130kinci olarak: Extremadura ve End\u00fcl\u00fcs i\u00e7 kesimlerine do\u011fru geni\u015fleme \u2014 burada kire\u00e7li topraklar kumlu Huelva profillerinin yerini al\u0131r ve kire\u00e7ta\u015f\u0131 \u00e7\u0131k\u0131nt\u0131lar\u0131ndan gelen y\u00fczey ta\u015f\u0131, g\u00fcney y\u00fcksek \u00e7al\u0131l\u0131k dikiminden \u00f6nce standart THOR 2.4 temizli\u011fini gerektirir.<\/div>\n<\/div>\n
\n
\ud83c\uddff\ud83c\udde6 G\u00fcney Afrika \u2014 Bat\u0131 Kap ve KwaZulu-Natal<\/span>
\nNH sezon d\u0131\u015f\u0131 arz\u0131<\/span><\/div>\n
G\u00fcney Afrika'n\u0131n yaban mersini end\u00fcstrisi, ta\u015f tipi risk matrisini en a\u00e7\u0131k \u015fekilde g\u00f6stermektedir. Cape Fold Belt jeolojisi (E-12, E-13), biti\u015fik alanlarda iki farkl\u0131 toprak tipi olu\u015fturmaktad\u0131r: Table Mountain Grubu kuvarsiti ve Cape graniti<\/strong> (Asidik toprakta kimyasal olarak inerttir \u2014 Mohs 6\u20137, s\u0131f\u0131r Ca\u00b2\u207a sal\u0131n\u0131m\u0131 \u2014 sadece fiziksel engelleme) ve Prekambriyen kire\u00e7ta\u015f\u0131 ve dolomit y\u00fczeyleri<\/strong> Cederberg, Swartberg ve Hex River s\u0131rada\u011flar\u0131nda (Mohs 3\u20134, y\u00fcksek Ca\u00b2\u207a sal\u0131n\u0131m\u0131 \u2014 yaban mersini i\u00e7in \u00f6l\u00fcmc\u00fcl pH). G\u00fcney Afrika'n\u0131n ba\u015fl\u0131ca y\u00fcksek \u00e7al\u0131l\u0131k b\u00f6lgesi olan Grabouw\/Elgin b\u00f6lgesinde yeni yaban mersini yeti\u015ftiricili\u011fi, ekimden \u00f6nce granit a\u011f\u0131rl\u0131kl\u0131 (d\u00fc\u015f\u00fck kimyasal risk) ve dolomit bula\u015fm\u0131\u015f (y\u00fcksek kimyasal risk) profilleri ay\u0131rt etmek i\u00e7in \u00f6nceden saha toprak ve ta\u015f analizi gerektirir. 15\u201330 cm derinlikte dolomit tespit edilen alanlarda, tamamen uzakla\u015ft\u0131r\u0131lmas\u0131 i\u00e7in THOR 3.0 temizli\u011fi gereklidir \u2014 Mohs 4 dolomit i\u00e7in THOR 2.4 yerine daha y\u00fcksek THOR 3.0 spesifikasyonu, sertlikten ziyade tam par\u00e7alanman\u0131n (CT-2100'\u00fcn g\u00f6zden ka\u00e7\u0131rd\u0131\u011f\u0131 art\u0131k topaklar olmamas\u0131) kesinli\u011fine duyulan ihtiya\u00e7tan kaynaklanmaktad\u0131r.<\/div>\n<\/div>\n<\/div>\n

<\/p>\n

Makine Sistemi \u2014 Yaban Mersini \u00d6zel Protokol\u00fc ve pH Do\u011frulama<\/h2>\n

\"PSW-3200<\/p>\n

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0<\/div>\n
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Orman temizli\u011fi \u00f6ncesi ta\u015f tipi ara\u015ft\u0131rmas\u0131 \u2014 yaban mersini i\u00e7in zorunlu (bu \u00fcr\u00fcne \u00f6zg\u00fc)<\/strong><\/p>\n

Makineyle herhangi bir i\u015flem yapmadan \u00f6nce, 10 m \u00d7 10 m'lik bir \u0131zgarada 40 cm derinli\u011fe kadar ta\u015f \u00f6rnekleri toplay\u0131n ve karbonat i\u00e7eri\u011fini test edin (HCl asit k\u00f6p\u00fcrme testi: kire\u00e7 ta\u015f\u0131 \u015fiddetli bir \u015fekilde k\u00f6p\u00fcr\u00fcr, granit\/kuvarsit k\u00f6p\u00fcrmez). Kire\u00e7 ta\u015f\u0131 i\u00e7eren b\u00f6lgeleri haritaland\u0131r\u0131n. Bu ara\u015ft\u0131rma, temizleme spesifikasyonunu belirler: kire\u00e7 ta\u015f\u0131 b\u00f6lgeleri i\u00e7in s\u0131f\u0131r toleransl\u0131 tam kald\u0131rma, granit b\u00f6lgeleri i\u00e7in ise standart yo\u011funluk azaltma. Atlamay\u0131n \u2014 dikim sonras\u0131 pH d\u00fczeltmesinin maliyeti, ara\u015ft\u0131rma maliyetini \u00e7ok a\u015fmaktad\u0131r.<\/p>\n<\/div>\n<\/div>\n

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1<\/div>\n
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THOR 2.4 veya 3.0<\/a> \u2014 kire\u00e7ta\u015f\u0131\/dolomitin tamamen par\u00e7alanm\u0131\u015f hali, 28\u201342 cm<\/strong><\/p>\n

Kire\u00e7ta\u015f\u0131 ve tebe\u015fir (Mohs 3\u20134): 2,0\u20132,5 km\/sa h\u0131zda THOR 2,4 yeterlidir. Dolomit veya daha sert karbonat: Tam par\u00e7alanman\u0131n kesinli\u011fi i\u00e7in THOR 3,0 gereklidir. Kritik: Kire\u00e7ta\u015f\u0131 i\u00e7eren alanlarda, hi\u00e7bir par\u00e7an\u0131n atlanmad\u0131\u011f\u0131ndan emin olmak i\u00e7in iki THOR ge\u00e7i\u015fi (kesi\u015fen y\u00f6nler) \u2014 geleneksel ta\u015f alanlar\u0131nda bir ge\u00e7i\u015f. Derinlik: Kuzey y\u00fcksek \u00e7al\u0131l\u0131klar\u0131 i\u00e7in 30\u201338 cm; tav\u015fan g\u00f6z\u00fc i\u00e7in 32\u201342 cm. Karbonat i\u00e7ermeyen granit\/kuvarsit ta\u015flar\u0131 i\u00e7in: ana\u00e7la e\u015fle\u015fen derinlikte standart tek ge\u00e7i\u015f.<\/p>\n<\/div>\n<\/div>\n

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2<\/div>\n
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CT-2100 ta\u015f toplay\u0131c\u0131<\/a> \u2014 s\u0131f\u0131r kal\u0131nt\u0131l\u0131 kire\u00e7ta\u015f\u0131 koleksiyonu<\/strong><\/p>\n

Kal\u0131c\u0131 toplama \u015fartt\u0131r. Kire\u00e7ta\u015f\u0131 alanlar\u0131nda, ba\u015fparmak b\u00fcy\u00fckl\u00fc\u011f\u00fcndeki par\u00e7alar bile tehlikeli bir pH y\u00fckselme b\u00f6lgesi olu\u015fturur; CT-2100 toplama e\u015fi\u011fi, 1 cm'den b\u00fcy\u00fck t\u00fcm par\u00e7alar\u0131 kapsamal\u0131d\u0131r. CT-2100 sonras\u0131 20 m \u00d7 20 m'lik bir \u0131zgarada 35 cm derinli\u011fe kadar pH prob ara\u015ft\u0131rmas\u0131: pH >5,8 g\u00f6steren herhangi bir nokta, hedefli yeniden temizleme gerektiren kal\u0131nt\u0131 karbonat aktivitesini g\u00f6sterir. Bu pH do\u011frulama ad\u0131m\u0131, t\u00fcm E serisi \u00fcr\u00fcnler aras\u0131nda yaban mersinine \u00f6zg\u00fcd\u00fcr; ba\u015fka hi\u00e7bir \u00fcr\u00fcn temizleme sonras\u0131 toprak kimyas\u0131 do\u011frulamas\u0131na ihtiya\u00e7 duymaz.<\/p>\n<\/div>\n<\/div>\n

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3<\/div>\n
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PSW-3200 rotavat\u00f6r<\/a> \u2014 Erikoid mikoriza olu\u015fumu i\u00e7in asitlendirilmi\u015f yatak olu\u015fturma<\/strong><\/p>\n

PSW-3200, 1000 RPM'de 22-28 cm ince toprakl\u0131 ekim yata\u011f\u0131 olu\u015fturur. \u0130\u00e7eri\u011finde \u015funlar bulunur: pH dengesini korumak i\u00e7in elementel k\u00fck\u00fcrt (standart: mevcut pH ve hedefe ba\u011fl\u0131 olarak 0,5-2,0 t\/ha); asitlendirilmi\u015f \u00e7am kabu\u011fu veya turba (erikoid mikorizal olu\u015fumu i\u00e7in minimum 30% organik fraksiyon); amonyum s\u00fclfat (pH uyumlu azot kayna\u011f\u0131). PSW-3200'\u00fcn bu katk\u0131 maddelerini homojen bir \u015fekilde kar\u0131\u015ft\u0131rmas\u0131, ta\u015fl\u0131 zeminde y\u00fczey uygulamas\u0131na g\u00f6re \u00f6nemli \u00f6l\u00e7\u00fcde daha etkilidir; ince toprak olu\u015fturma, k\u00f6k b\u00f6lgesinde e\u015fit da\u011f\u0131l\u0131m\u0131 sa\u011flar.<\/p>\n<\/div>\n<\/div>\n<\/div>\n

<\/p>\n

S\u0131k\u00e7a Sorulan Sorular<\/h2>\n
\n
\nYaban mersini \u00e7iftli\u011fi i\u00e7in kaya k\u0131r\u0131c\u0131 \u2014 granit ta\u015f\u0131 yaban mersini i\u00e7in kire\u00e7 ta\u015f\u0131 kadar tehlikeli mi, yoksa ta\u015f t\u00fcr\u00fc ger\u00e7ekten temizleme aciliyetini de\u011fi\u015ftiriyor mu?<\/summary>\n

Ta\u015f t\u00fcr\u00fc, yaban mersini i\u00e7in temizleme aciliyetini, bu k\u0131lavuzdaki di\u011fer hi\u00e7bir \u00fcr\u00fcnde benzeri olmayan bir \u015fekilde temelden de\u011fi\u015ftirir. Granit, kuvarsit ve \u00e7akmakta\u015f\u0131 asidik topraklarda kimyasal olarak inerttir; kalsiyum veya alkalile\u015ftirici iyonlar salmazlar ve bu nedenle toprak pH'\u0131n\u0131 etkilemezler. Yaban mersini \u00fczerindeki etkileri yaln\u0131zca fizikseldir: k\u00f6k \u00f6rt\u00fcs\u00fcn\u00fcn k\u0131s\u0131tlanmas\u0131, damlama band\u0131 hasar\u0131 ve mikorizal a\u011f s\u00fcreklili\u011fini etkileyen nem heterojenli\u011fi. Bu fiziksel etkiler \u00f6nemlidir ve temizlemeyi hakl\u0131 \u00e7\u0131kar\u0131r, ancak kire\u00e7ta\u015f\u0131 \u00e7\u00f6z\u00fcnmesi gibi bitki i\u00e7in \u00f6l\u00fcmc\u00fcl de\u011fildirler. Sadece granit i\u00e7eren ta\u015fl\u0131 toprakta yeti\u015fen bir yaban mersini bitkisi tipik olarak verimde azalma ve baz\u0131 yer yer mikorizal a\u011f bozulmas\u0131 g\u00f6sterecektir, ancak hayatta kalacak, \u00fcr\u00fcn verecek ve y\u00f6netime yan\u0131t verecektir. Kire\u00e7ta\u015f\u0131 par\u00e7ac\u0131klar\u0131yla kirlenmi\u015f toprakta yeti\u015fen bir yaban mersini bitkisi, toprak \u00fcst\u00fcnde uygulanan herhangi bir y\u00f6netim m\u00fcdahalesinden ba\u011f\u0131ms\u0131z olarak, pH y\u00fckselme b\u00f6lgesi geni\u015fledik\u00e7e damarlar aras\u0131 klorozdan giderek \u00f6lecektir. Bu nedenle, \u00f6n temizleme ta\u015f tipi ara\u015ft\u0131rmas\u0131 (tarla \u00f6rneklerinde HCl k\u00f6p\u00fcrme testi) yaban mersini i\u00e7in bir formalite de\u011fil; standart temizleme mi yoksa s\u0131f\u0131r toleransl\u0131 tam karbonat giderme mi gerekti\u011fini belirleyen te\u015fhis y\u00f6ntemidir. Bu serideki ba\u015fka hi\u00e7bir \u00fcr\u00fcn bu ta\u015f tipi ayr\u0131m\u0131n\u0131 gerektirmez.<\/p>\n<\/details>\n

\nDemir \u015felat (EDTA, DTPA, EDDHA) i\u00e7eren yaprak veya toprak uygulamalar\u0131, kire\u00e7ta\u015f\u0131 pH y\u00fckselmesinden kaynaklanan klorozu d\u00fczeltebilir mi, yoksa tek \u00e7\u00f6z\u00fcm temizleme mi?<\/summary>\n

Demir \u015felat uygulamalar\u0131 ge\u00e7ici semptomatik rahatlama sa\u011flar ancak yerle\u015fik bir ekimde altta yatan kire\u00e7ta\u015f\u0131 pH sorununu d\u00fczeltemez. Toprak sulama veya yaprak spreyi olarak uygulanan EDDHA (pH 9'a kadar etkili, en pH stabil \u015felatl\u0131 demir), klorozlu yaban mersini yapraklar\u0131na 2-4 hafta i\u00e7inde ye\u015fil rengi geri kazand\u0131r\u0131r; ancak kire\u00e7ta\u015f\u0131 \u00e7\u00f6z\u00fcnmesi devam etti\u011fi i\u00e7in kloroz geri d\u00f6nmeden \u00f6nce etki sadece 4-6 hafta s\u00fcrer. \u00d6nemli kire\u00e7ta\u015f\u0131 kirlili\u011fine sahip 1 hektarl\u0131k bir yaban mersini ekiminde demir \u015felat tedavisinin y\u0131ll\u0131k maliyeti: uygulama oran\u0131na ve \u015felat t\u00fcr\u00fcne ba\u011fl\u0131 olarak yakla\u015f\u0131k 800-1800 \u20ac\/ha\/y\u0131l. 15 y\u0131ll\u0131k bir yaban mersini \u00fcretim d\u00f6ng\u00fcs\u00fc boyunca: k\u00f6k nedeni ele almayan d\u00fczeltici tedavi maliyetleri 12.000-27.000 \u20ac\/ha. Ekim \u00f6ncesi kire\u00e7ta\u015f\u0131 temizleme maliyeti: 1500-3000 \u20ac\/ha. D\u00fczeltici tedavi yolu, \u00f6nleyici temizleme yoluna g\u00f6re 4-9 kat daha pahal\u0131d\u0131r ve \u015felat tedavisi uygulansa bile, kire\u00e7ta\u015f\u0131ndan etkilenen bitkilerde verim, etkilenmemi\u015f e\u015fde\u011ferlerine g\u00f6re genellikle 20-401 TP5T daha d\u00fc\u015f\u00fck kal\u0131r \u00e7\u00fcnk\u00fc erikoid mikorizal a\u011f, demir \u015felat uygulamas\u0131yla restore edilemez. Karbonat ta\u015f\u0131 bulunan alanlarda ekonomik olarak mant\u0131kl\u0131 tek yakla\u015f\u0131m, temizleme yat\u0131r\u0131m\u0131d\u0131r.<\/p>\n<\/details>\n

\nY\u00fckseltilmi\u015f yatakl\u0131 yaban mersini yeti\u015ftiricili\u011fi (\u0130spanya ve Fas'ta standart y\u00f6ntem), bitki k\u00f6kleri ithal edilmi\u015f y\u00fckseltilmi\u015f yeti\u015ftirme ortam\u0131nda b\u00fcy\u00fcd\u00fc\u011f\u00fc i\u00e7in ta\u015f temizleme ihtiyac\u0131n\u0131 ortadan kald\u0131r\u0131r m\u0131?<\/summary>\n

Y\u00fckseltilmi\u015f yatakl\u0131 yeti\u015ftirme, yaban mersini i\u00e7in ta\u015f y\u00f6netimi gereksinimini \u00f6nemli \u00f6l\u00e7\u00fcde azalt\u0131r ancak tamamen ortadan kald\u0131rmaz. Huelva modelinde \u2014 plastik mal\u00e7 \u00fczerine ithal asitlendirilmi\u015f turba\/\u00e7am kabu\u011fu substrat\u0131ndan olu\u015fan 30-40 cm'lik y\u00fckseltilmi\u015f yataklarda \u2014 bitki k\u00f6kleri ba\u015flang\u0131\u00e7ta yaln\u0131zca ithal temiz substratta b\u00fcy\u00fcr. Bununla birlikte, iki senaryo hala alttaki do\u011fal topra\u011fa dikkat edilmesini gerektirir. Birincisi, 4-6 y\u0131l i\u00e7inde, en g\u00fc\u00e7l\u00fc bitkiler, \u00f6zellikle mal\u00e7 ve taban haz\u0131rl\u0131\u011f\u0131n\u0131n k\u00f6k eri\u015fimine izin verdi\u011fi yerlerde, y\u00fckseltilmi\u015f yata\u011f\u0131n alt\u0131na, do\u011fal topra\u011fa n\u00fcfuz eden k\u00f6kler geli\u015ftirir. Do\u011fal toprak 15-25 cm derinlikte (y\u00fckseltilmi\u015f yatak taban\u0131n\u0131n alt\u0131ndaki b\u00f6lge) kire\u00e7 ta\u015f\u0131 i\u00e7eriyorsa, bu n\u00fcfuz eden k\u00f6kler pH y\u00fckselmesi sorunuyla kar\u015f\u0131la\u015f\u0131r. \u0130kincisi, yatak kenarlar\u0131na do\u011fru b\u00fcy\u00fcyen kom\u015fu bitkilerden gelen yanal k\u00f6kler, yatak \u00e7evresi boyunca do\u011fal toprakla temas eder. 20-40 cm'lik do\u011fal toprak horizonunda kire\u00e7ta\u015f\u0131 bulundu\u011fu do\u011frulanan alanlarda y\u00fckseltilmi\u015f yatak uygulamalar\u0131 i\u00e7in, y\u00fckseltilmi\u015f yatak yap\u0131m\u0131ndan \u00f6nce do\u011fal topra\u011f\u0131n THOR 2.4 y\u00f6ntemiyle temizlenmesi, bu uzun vadeli k\u00f6k penetrasyon risklerini, y\u00fckseltilmi\u015f yatak kurulum yat\u0131r\u0131m\u0131na (tipik olarak 15.000-25.000 \u20ac\/ha) k\u0131yasla minimum maliyetle ortadan kald\u0131r\u0131r. Granit veya kuvarsit ta\u015f\u0131 bulunan ve karbonat i\u00e7eri\u011fi olmayan alanlarda, y\u00fckseltilmi\u015f yatak ekimi ta\u015f y\u00f6netimi gereksinimini etkili bir \u015fekilde ortadan kald\u0131r\u0131r; y\u00fckseltilmi\u015f substrat k\u00f6k ortam\u0131n\u0131 sa\u011flar ve do\u011fal toprakla temas d\u00fc\u015f\u00fck risklidir.<\/p>\n<\/details>\n

\nYaban mersini hasad\u0131nda mekanik hasat y\u00f6ntemiyle olu\u015fan ta\u015f kontaminasyon riski, E-14'te a\u00e7\u0131klanan f\u0131nd\u0131k vakumlu hasat makinesi kontaminasyon riskiyle nas\u0131l kar\u015f\u0131la\u015ft\u0131r\u0131l\u0131r?<\/summary>\n

Yaban mersini mekanik hasad\u0131 (d\u00f6ner toplama ba\u015fl\u0131\u011f\u0131 veya s\u00fcrekli yakalama-konvey\u00f6r sistemi), E-14'te a\u00e7\u0131klanan f\u0131nd\u0131k vakumlu hasat makinesi problemine benzer ancak farkl\u0131 ticari sonu\u00e7lara sahip bir ta\u015f kontaminasyonu riski olu\u015fturur. F\u0131nd\u0131k kontaminasyonu, yabanc\u0131 madde y\u00fczdesine ba\u011fl\u0131 olarak i\u015fleme tesisinde reddedilmeye neden olur. Yaban mersini kontaminasyonu iki t\u00fcr kalite hatas\u0131na neden olur: (1) taze meyve paketine giren ta\u015f par\u00e7alar\u0131, perakende sat\u0131\u015fta g\u00f6r\u00fclebilen tek tek meyvelerde fiziksel hasara (ezilme, kabuk delinmesi) neden olur - g\u00f6r\u00fcn\u00fcr ta\u015f par\u00e7alar\u0131 i\u00e7eren taze pazar paketi, \u0130ngiltere ve AB'deki premium s\u00fcpermarketlerde t\u00fcketici \u015fikayetine ve \u00fcr\u00fcn geri \u00e7a\u011f\u0131rmaya neden olur; (2) i\u015fleme ak\u0131\u015flar\u0131ndaki (dondurulmu\u015f yaban mersini, meyve suyu, p\u00fcre) ta\u015f par\u00e7alar\u0131, i\u015fleme ekipman\u0131na zarar verebilir ve geri \u00e7a\u011f\u0131rmaya yol a\u00e7an parti kontaminasyonuna neden olabilir. Ticari ciddiyet kanala g\u00f6re de\u011fi\u015fir: taze perakende kontaminasyonu orant\u0131s\u0131z itibar sonu\u00e7lar\u0131na yol a\u00e7ar (meyve paketlerindeki ta\u015flarla ilgili viral sosyal medya \u015fikayetleri); i\u015fleme kanal\u0131 kontaminasyonu parti geri \u00e7ekme maliyetine yol a\u00e7ar. Y\u00fczey ta\u015f temizleme ile BlackBird kaya t\u0131rm\u0131\u011f\u0131<\/a> Mekanik hasat sezonundan \u00f6nce, f\u0131nd\u0131k i\u00e7in a\u00e7\u0131klanan hasat \u00f6ncesi y\u00fczey ge\u00e7i\u015fi, iyi y\u00f6netilen \u015eili ve Pasifik Kuzeybat\u0131 yaban mersini \u00e7iftliklerinde standart bir uygulamad\u0131r.<\/p>\n<\/details>\n

\nYaban mersini \u00e7iftli\u011finde ta\u015f temizleme i\u015fleminin, alternatif olarak kullan\u0131lan \u015felat tedavisine k\u0131yasla ger\u00e7ek\u00e7i yat\u0131r\u0131m getirisi (ROI) nedir?<\/summary>\n

Washington Eyaleti'nde, 15-30 cm derinlikte kire\u00e7ta\u015f\u0131 par\u00e7alar\u0131n\u0131n bulundu\u011fu buzul tortusu \u00fczerinde 3 hektarl\u0131k bir kuzey y\u00fcksek \u00e7al\u0131 yaban mersini ekimi i\u00e7in: Ekim \u00f6ncesi temizleme maliyeti (THOR 2.4 + CT-2100, 3 ha): yakla\u015f\u0131k $6.000\u20139.000. Alternatif d\u00fczeltici yol maliyeti: Kire\u00e7ta\u015f\u0131 kirlili\u011fi belirtileri g\u00f6steren ekim alan\u0131n\u0131n 30%'sine demir \u015felat uygulamas\u0131 (EDDHA toprak sulama, y\u0131ll\u0131k): yakla\u015f\u0131k $1.400\u20132.600\/y\u0131l \u00d7 14 kalan sezon = $19.600\u201336.400. Etkilenen bitkilerdeki verim kayb\u0131 da hesaba kat\u0131ld\u0131\u011f\u0131nda (30% ekim alan\u0131nda muhafazakar bir yakla\u015f\u0131mla 25% verim d\u00fc\u015f\u00fc\u015f\u00fc): yakla\u015f\u0131k 13,5 ton \u00d7 $0,65\/lb \u00e7iftlik kap\u0131s\u0131 ortalama fiyat\u0131 \u00d7 25% \u00d7 14 y\u0131l = $17.300 k\u00fcm\u00fclatif verim kayb\u0131. Toplam d\u00fczeltici yol maliyeti: ekim \u00f6mr\u00fc boyunca $37.000\u201354.000. Maliyet avantaj\u0131: 3 hektarl\u0131k ekim alan\u0131 ba\u015f\u0131na bug\u00fcnk\u00fc de\u011fer tasarrufu olarak $31.000\u201345.000. Yat\u0131r\u0131m getirisi oran\u0131: yaln\u0131zca \u015felat ve verim kayb\u0131 maliyetlerinden ka\u00e7\u0131n\u0131ld\u0131\u011f\u0131nda 4:1 ila 6:1. Bu hesaplamalar muhafazakar parametreler kullan\u0131larak yap\u0131lm\u0131\u015ft\u0131r; $1,20\u20131,60\/lb fiyatla premium taze pazar s\u00f6zle\u015fmeleri olan yeti\u015ftiriciler, verim kayb\u0131 ve kalite d\u00fc\u015f\u00fc\u015f\u00fcn\u00fcn etkileri orant\u0131l\u0131 olarak daha b\u00fcy\u00fck oldu\u011fu i\u00e7in \u00f6nemli \u00f6l\u00e7\u00fcde daha y\u00fcksek yat\u0131r\u0131m getirisi elde ederler. Korea Watanabe, ta\u015f t\u00fcr\u00fc de\u011ferlendirmesi sonucunda kire\u00e7 ta\u015f\u0131 veya karbonat riski tespit edilen her t\u00fcrl\u00fc yaban mersini yeti\u015ftirme projesi i\u00e7in sahaya \u00f6zel bir yat\u0131r\u0131m getirisi (ROI) hesaplamas\u0131 haz\u0131rlayabilir.<\/p>\n<\/details>\n<\/div>\n

<\/p>\n

\n
\n
\n

Yaban Mersini \u00c7iftli\u011fi \u0130\u00e7in Kaya K\u0131rma Makinesi \u2014 Ta\u015f Tipi Ara\u015ft\u0131rmas\u0131 ve Kire\u00e7ta\u015f\u0131 Kald\u0131rma Protokol\u00fc<\/p>\n

Yaban mersini t\u00fcr\u00fc + ta\u015f inceleme sonu\u00e7lar\u0131 (karbonatl\u0131 vs karbonats\u0131z) + b\u00f6lgesel jeoloji + mevcut trakt\u00f6r beygir g\u00fcc\u00fc \u2192 Korea Watanabe \u015funlar\u0131 sa\u011flar: yaban mersini \u00e7iftli\u011fi i\u00e7in kaya k\u0131r\u0131c\u0131<\/a> Siteniz i\u00e7in spesifikasyon, s\u0131f\u0131r toleransl\u0131 kire\u00e7 ta\u015f\u0131 temizleme protokol\u00fc ve \u015felatlama ile temizleme y\u00f6ntemlerinin yat\u0131r\u0131m getirisi kar\u015f\u0131la\u015ft\u0131rmas\u0131.<\/p>\n

\n<\/div>\n

Yaban Mersini Temizleme \u00d6zelliklerini Edinin<\/a><\/div>\n<\/div>\n<\/div>\n

Edit\u00f6r: Cxm<\/p>\n<\/div>","protected":false},"excerpt":{"rendered":"

YABAN MERS\u0130N\u0130 \u00c7\u0130FTL\u0130\u011e\u0130 UYGULAMASI Yaban Mersini \u00c7iftli\u011fi i\u00e7in Kaya K\u0131r\u0131c\u0131 \u2014 Asidik Toprak K\u00f6k B\u00f6lgesi K\u0131lavuzu Bir kire\u00e7 ta\u015f\u0131 \u00e7ak\u0131l\u0131 yerel pH'\u0131 7,0'a y\u00fckseltir \u2014 bu noktada hi\u00e7bir g\u00fcbre, \u00fczerindeki yaban mersinine demir eri\u015filebilirli\u011fini geri kazand\u0131ramaz. pH 4,5\u20135,5 Gerekli toprak pH aral\u0131\u011f\u0131 6\u20138 y\u0131l Verimli fide \u00f6mr\u00fc 1 \u00e7ak\u0131l Kire\u00e7 ta\u015f\u0131 = yerel pH'\u0131 d\u00fc\u015f\u00fcr\u00fcr [\u2026]<\/p>","protected":false},"author":1,"featured_media":0,"comment_status":"open","ping_status":"open","sticky":false,"template":"","format":"standard","meta":{"_et_pb_use_builder":"","_et_pb_old_content":"","_et_gb_content_width":"","footnotes":""},"categories":[31],"tags":[],"class_list":["post-961","post","type-post","status-publish","format-standard","hentry","category-application-and-technical-guid"],"_links":{"self":[{"href":"https:\/\/rock-crusher-tractor.com\/tr\/wp-json\/wp\/v2\/posts\/961","targetHints":{"allow":["GET"]}}],"collection":[{"href":"https:\/\/rock-crusher-tractor.com\/tr\/wp-json\/wp\/v2\/posts"}],"about":[{"href":"https:\/\/rock-crusher-tractor.com\/tr\/wp-json\/wp\/v2\/types\/post"}],"author":[{"embeddable":true,"href":"https:\/\/rock-crusher-tractor.com\/tr\/wp-json\/wp\/v2\/users\/1"}],"replies":[{"embeddable":true,"href":"https:\/\/rock-crusher-tractor.com\/tr\/wp-json\/wp\/v2\/comments?post=961"}],"version-history":[{"count":2,"href":"https:\/\/rock-crusher-tractor.com\/tr\/wp-json\/wp\/v2\/posts\/961\/revisions"}],"predecessor-version":[{"id":963,"href":"https:\/\/rock-crusher-tractor.com\/tr\/wp-json\/wp\/v2\/posts\/961\/revisions\/963"}],"wp:attachment":[{"href":"https:\/\/rock-crusher-tractor.com\/tr\/wp-json\/wp\/v2\/media?parent=961"}],"wp:term":[{"taxonomy":"category","embeddable":true,"href":"https:\/\/rock-crusher-tractor.com\/tr\/wp-json\/wp\/v2\/categories?post=961"},{"taxonomy":"post_tag","embeddable":true,"href":"https:\/\/rock-crusher-tractor.com\/tr\/wp-json\/wp\/v2\/tags?post=961"}],"curies":[{"name":"wp","href":"https:\/\/api.w.org\/{rel}","templated":true}]}}