scholarly journals Population Abundance and Distribution of Ectoparasitic Plant Nematodes Associated with Apple Trees (Malus domestica) in Apple Belts of Kashmir, India

Author(s):  
G. M. Lone ◽  
F. A. Zaki ◽  
S. S. Pathania ◽  
Sajad Mohi
Forests ◽  
2021 ◽  
Vol 12 (3) ◽  
pp. 367
Author(s):  
Mateja Kišek ◽  
Kristjan Jarni ◽  
Robert Brus

This study focuses on the morphological and genetic characteristics of European crab apple (Malus sylvestris (L.) Mill.) and the occurrence of hybrids in its populations. We analyzed a total of 107 putative European crab apple trees in Slovenia: 92 from nine natural populations, five from a seed stand and 10 from a stand of unnatural origin. We also included 18 domesticated apple trees (Malus × domestica Borkh.) and two Japanese flowering crab apple trees (Malusfloribunda van Houtte) as outliers. The trees were classified into groups of European crab apples, hybrids and domesticated apples according to their morphological and genetic characteristics. Classification based on morphological traits produced different results (58.75% European crab apple, 37.11% hybrids and 4.14% domesticated apple) compared to those based on genetic analysis (70.10% European crab apple, 21.64% hybrids and 8.26% domesticated apple). When genetic and morphological characteristics were combined, only 40.20% of the trees were classified as European crab apple, and an additional group of feral cultivars of domesticated apples (6.18%) was identified. The analysis revealed that hybridization with domesticated apple is taking place in all studied natural European crab apple populations; however, hybrids and feral cultivars only occur to a limited extent. When introducing European crab apple into forests in the future, only genetically verified forest reproductive material obtained exclusively from suitable seed stands should be used.


1997 ◽  
Vol 122 (6) ◽  
pp. 837-840 ◽  
Author(s):  
Matej Stopar ◽  
Brent L. Black ◽  
Martin J. Bukovac

The effects of NAA, BA, or Accel on CO2 assimilation of shoot leaves of mature bearing Redchief `Delicious' and `Empire' apple (Malus ×domestica Borkh.) trees were evaluated over two seasons. BA at 50 mg·L-1 did not significantly affect any of the gas-exchange parameters measured. NAA (15 mg·L-1) consistently suppressed CO2 assimilation rate (from ≈10% to 24% below that of the control). This suppression was NAA-concentration dependent, continued for >15 days after treatment, and was completely overcome in `Empire', but only partially or not at all in `Delicious' when BA was combined with NAA. These results are discussed in relation to fruit thinning and NAA-induced inhibition of fruit growth in spur-type `Delicious'. Chemical names used: 2-(1-napthyl) acetic acid (NAA); N-(phenyl)-1H-purine-6-amine (BA); BA + gibberellin A (GA)4+7 (Accel).


Primates ◽  
2019 ◽  
Vol 60 (5) ◽  
pp. 437-448 ◽  
Author(s):  
Phuntsho Thinley ◽  
Tshewang Norbu ◽  
Rajanathan Rajaratnam ◽  
Karl Vernes ◽  
Kezang Wangchuk ◽  
...  

2016 ◽  
Vol 34 ◽  
pp. 151-164 ◽  
Author(s):  
Mohammed Y. Said ◽  
Joseph O. Ogutu ◽  
Shem C. Kifugo ◽  
Ogeli Makui ◽  
Robin S. Reid ◽  
...  

1981 ◽  
Vol 61 (2) ◽  
pp. 295-302 ◽  
Author(s):  
G. H. NEILSEN ◽  
E. HOGUE ◽  
B. G. DROUGHT

In 1975, hydrated lime and calcium sulfate were applied to a Rutland gravelly sandy loam under the canopy of mature apple trees (Malus domestica Borkh. ’Spartan’) on M16 at 3000, 6000, 3 × 2000 and at 3000, 6000, 3 × 4000 kg/ha, respectively, pH and exchangeable Ca, Mg and Mn were measured in the soil sampled in 1979 at 10-cm intervals to a 60-cm depth for each of the check, 6000 kg/ha Ca(OH)2 and 12 000 kg/ha gypsum treatments. The acidity of the surface soil was decreased significantly in the 6000 kg/ha Ca(OH)2 treatment. Negligible soil Ca accumulation occurred below the surface 10-cm depth for any treatment. Soil Mn was decreased from the surface to the 20-cm level in the Ca(OH)2 treatment while soil Mg was decreased from the surface to the 30-cm level in the gypsum treatment. Fruit Ca concentration at harvest, 1975–1979 was not increased by soil Ca treatments. Leaf Mg was often reduced by soil gpysum applications in excess of 3000 kg/ha. Leaf Mn reduction did not occur until the 4th and 5th yr of the experiment in the 6000 and the 3 × 2000 kg/ha Ca(OH)2 treatments.


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