‫آﺳﺘﺎ‬ ‫ﺣﺪ‬ ‫ﺗﻌﯿﯿﻦ‬ ‫و‬ ‫ارزﯾﺎﺑﯽ‬ ‫ﺷﻮري‬ ‫ﺑﻪ‬ ‫ﺗﺤﻤﻞ‬ ‫ﻧﻪ‬ ‫ﺗﻮده‬ ‫ﺑﺮﺧﯽ‬ ‫ﺷﻨﺒﻠﯿﻠﻪ‬ ‫ﻫﺎي‬ ) Trigonella foenumgraecum ( ‫ﺷﺪن‬ ‫ﺳﺒﺰ‬ ‫ﻣﺮﺣﻠﻪ‬ ‫در‬ ‫ﮔﯿﺎﻫﭽﻪ‬

Keywords: Legumes, Linear model, Seedling, Sigmoidal model

Introduction: Fenugreek, is a medicinal plant that has been considered as a salt tolerant crop. This research was conducted to investigate the effects of salt stress on seedling emergence characteristics and determination of the salt tolerance threshold, declivity of emergence and salt tolerance index of some fenugreek ecotypes. 
Material and Methods: Seeds of five ecotypes (Ardestani, Isfahani, hendi, Mashhadi, Neyrizi) were subjected to seven levels of salinity (0.5, 3, 6, 9, 12, 15 and 18 dS/m) in a factorial experiment based on a completely randomized design with three replications. In this research, experimental models (linear, sigmoidal, exponential and multi-component) were used. 
Results: Results showed that increasing levels of salinity decreased seedling emergence percentage and rate. In Ardestani and Isfahani ecotypes, increase of salinity up to 3 dS/m had no effect on seedling emergence percentage and thereafter, decreased it, significantly. The maximum seedling emergence percentage (94.62%) belonged to Hendi in control treatment. Hendi ecotype had also the highest emergence percentage (25.81%) at 18 dS/m. Although the highest seedling emergence rate (5.93 per day) belonged to Mashhadi ecotype in control treatment, it didn't show any significant difference to Hendi, Neyrizi and Isfahani ecotypes. In Ardestani, Mashhadi and Neyrizi ecotypes, seedling length decreased significantly with increasing salinity, but this decrease was not significant in Isfahani ecotype between salinities of 3 and 6 dS/m and also 12 and 15 dS/m. In Hendi ecotype, seedling length at 3 dS/m was similar to control, but higher salinities caused a significant reduction. The maximum value of seedling vigor index (20.44) belonged to Mashhadi and Neyrizi ecotypes in control treatment and Ardestani ecotype had the lowest one (0.39) at 18 dS/m. Results showed that seedling dry weight was first unchanged up to salinity level of 3 dS/m and then gradually decreased with increasing salinity. In Hendi and Neyrizi ecotypes, applying salinities higher than 6 dS/m, gradually decreased seedling dry weight. The salt tolerance threshold of fenugreek for Ardestani, Isfahani, Hindi, Mashhadi and Neyrizi ecotypes was 4.69, 4.90, 7.83, 1.69 and 1.57 dS/m, respectively. Thus, the highest salt tolerance threshold (7.83 dS/m) and the declivity of emergence percentage (7.55%) was obtained from Hendi ecotype and the lowest one from Neyrizi ecotype (1.57 and 4.63 dS/m, respectively). Results of nonlinear models showed that the highest salinity in which 50 percent of seedlings emerged was obtained in Hendi ecotype (14.24 dS/m). 

Conclusion:

Based on the results, comparing the salt tolerance index of fenugreek ecotypes and also evaluating of some experimental models showed that Hendi ecotype may be introduced as the most tolerant ecotype to salinity stress at the emergence stage to exploit saline soil and water resources. 

In these equations, Y: relative yield, Y m : maximum yield under non-saline conditions, a 0 : salt tolerance threshold, I: emergence declivity rate, EC 50 : maximum salninty at which the yield is decreased by 50 perecent, p: experimental constant, s: slope of the curve, and a an b denote: equation constants. 

‫ﻫﻤﮑﺎران‬ ‫و‬ ‫ﺑﻨﺎﮐﺎر‬


‫ﭼﮑﯿﺪه‬ ‫ﻣﺒﺴﻮط‬ ‫ﻣﻘﺪﻣﻪ‬ : ‫ﺷﻨﺒﻠﯿﻠﻪ‬ ‫داروﯾﯽ‬ ‫ﮔﯿﺎﻫﺎن‬ ‫از‬ ‫ﯾﮑﯽ‬ ، ‫اﺳﺖ‬ ‫ﺑﻮده‬ ‫ﺗﻮﺟﻪ‬ ‫ﻣﻮرد‬ ‫ﺷﻮري‬ ‫ﺑﻪ‬ ‫ﻣﺘﺤﻤﻞ‬ ‫ﮔﯿﺎه‬ ‫ﯾﮏ‬ ‫ﻋﻨﻮان‬ ‫ﺑﻪ‬ ‫ﮐﻪ‬ ‫اﺳﺖ‬ . ‫ﺑﻪ‬ ‫ﺗﺤﻘﯿﻖ،‬ ‫اﯾﻦ‬ ‫وﯾﮋﮔﯽ‬ ‫ﺑﺮ‬ ‫ﺷﻮري‬ ‫ﺗﻨﺶ‬ ‫اﺛﺮات‬ ‫ﺑﺮرﺳﯽ‬ ‫ﻣﻨﻈﻮر‬ ‫ﮔﯿﺎﻫﭽﻪ‬ ‫ﺷﺪن‬ ‫ﺳﺒﺰ‬ ‫ﻫﺎي‬ ‫و‬ ‫ﺷﺪن‬ ‫ﺳﺒﺰ‬ ‫ﮐﺎﻫﺶ‬ ‫ﺷﯿﺐ‬ ‫ﺷﻮري،‬ ‫ﺑﻪ‬ ‫ﺗﺤﻤﻞ‬ ‫آﺳﺘﺎﻧﻪ‬ ‫ﺣﺪ‬ ‫ﺗﻌﯿﯿﻦ‬ ‫و‬ ‫ﺗﻮده‬ ‫ﺑﺮﺧﯽ‬ ‫ﺷﻮري‬ ‫ﺑﻪ‬ ‫ﺗﺤﻤﻞ‬ ‫ﺷﺎﺧﺺ‬ ‫ﮔﺮﻓﺖ‬ ‫اﻧﺠﺎم‬ ‫ﺷﻨﺒﻠﯿﻠﻪ‬ ‫ﻫﺎي‬ .

  
	‫و‬	15	12 ،	9 ،	6 ،	3 ،	) 5 / 0 ،	‫ﺷﻮري‬ ‫ﺳﻄﺢ‬ ‫ﻫﻔﺖ‬ ‫در‬	(	‫رﯾﺰي‬	‫ﻧﯽ‬	‫و‬	) ‫ﻣﺸﻬﺪي‬ ‫ﻫﻨﺪي،‬ ‫اﺻﻔﻬﺎﻧﯽ،‬ ‫اردﺳﺘﺎﻧﯽ،‬	‫ﺗﻮده‬	‫ﭘﻨﺞ‬ ‫ﺑﺬرﻫﺎي‬	:	‫ﻫﺎ‬	‫روش‬ ‫و‬ ‫ﻣﻮاد‬
	‫ﺗﺠﺮﺑﯽ‬ ‫ﻫﺎي‬	‫ﻣﺪل‬ ‫از‬ ‫ﺗﺤﻘﯿﻖ،‬ ‫اﯾﻦ‬ ‫در‬	.	‫ﮔﺮﻓﺘﻨﺪ‬ ‫ﻗﺮار‬ ‫ﺗﮑﺮار‬ ‫ﺳﻪ‬ ‫ﺑﺎ‬ ‫ﺗﺼﺎدﻓﯽ‬	ً ‫ﮐﺎﻣﻼ‬	‫ﻃﺮح‬ ‫ﻗﺎﻟﺐ‬ ‫در‬	‫ﻓﺎﮐﺘﻮرﯾﻞ‬ ‫آزﻣﺎﯾﺶ‬ ‫ﺑﺼﻮرت‬	dS/m (	18
																	.	‫ﺷﺪ‬ ‫اﺳﺘﻔﺎده‬	(	‫ﺟﺰﺋﯽ‬ ‫ﭼﻨﺪ‬ ‫و‬ ‫ﻧﻤﺎﯾﯽ‬ ‫ﺳﯿﮕﻤﻮﺋﯿﺪي،‬ ‫ﺧﻄﯽ،‬	)
								‫ﯾﺎﻓﺖ‬ ‫ﮐﺎﻫﺶ‬							:	‫ﻫﺎ‬	‫ﯾﺎﻓﺘﻪ‬

‫ﮔﯿﺎﻫﭽﻪ‬ ‫ﺷﺪن‬ ‫ﺳﺒﺰ‬ ‫ﺳﺮﻋﺖ‬ ‫و‬ ‫درﺻﺪ‬ ‫ﺷﻮري،‬ ‫اﻓﺰاﯾﺶ‬ ‫ﺑﺎ‬ ‫ﮐﻪ‬ ‫داد‬ ‫ﻧﺸﺎن‬ ‫ﻧﺘﺎﯾﺞ‬ . ‫ﺗﻮده‬ ‫در‬ ‫اﺻﻔﻬﺎﻧﯽ،‬ ‫و‬ ‫اردﺳﺘﺎﻧﯽ‬ ‫ﻫﺎي‬

  
	‫ﺳﺒﺰ‬ ‫درﺻﺪ‬ ‫ﺑﯿﺸﺘﺮﯾﻦ‬	.	‫ﻣﻌﻨﯽ‬ ‫ﮐﺎﻫﺶ‬ ‫آن‬ ‫از‬ ‫ﭘﺲ‬ ‫و‬ ‫ﻧﺪاﺷﺖ‬ ‫ﮐﺮد‬ ‫ﭘﯿﺪا‬ ‫داري‬	‫ﮔﯿﺎﻫﭽﻪ‬	‫ﺷﺪن‬ ‫ﺳﺒﺰ‬	‫درﺻﺪ‬ ‫ﺑﺮ‬	‫ﺗﺎﺛﯿﺮي‬	dS/m 3	‫ﺗﺎ‬ ‫ﺷﻮري‬ ‫اﻓﺰاﯾﺶ‬
	/ 25	) 81	‫ﺷﺪن‬ ‫ﺳﺒﺰ‬ ‫درﺻﺪ‬ ‫ﺑﯿﺸﺘﺮﯾﻦ‬ ‫ﻧﯿﺰ‬	18	dS/m	‫در‬ ‫ﻫﻨﺪي‬ ‫ﺗﻮده‬	.	‫ﺷ‬ ‫ﺗﯿﻤﺎر‬ ‫در‬ ‫ﻫﻨﺪي‬ ‫ﺗﻮده‬ ‫از‬ ‫آﻣﺪ‬ ‫ﺑﺪﺳﺖ‬ ‫ﺎﻫﺪ‬	‫درﺻﺪ‬ (	62 / 94	)	‫ﺷﺪن‬
	‫اﻣﺎ‬ ‫ﺑﻮد،‬					(	‫روز‬ ‫در‬ ‫ﻋﺪد‬	5	) 93 /	‫ﮔﯿﺎﻫﭽﻪ‬ ‫ﺷﺪن‬ ‫ﺳﺒﺰ‬ ‫ﺳﺮﻋﺖ‬ ‫ﺑﯿﺸﺘﺮﯾﻦ‬ ‫اﮔﺮﭼﻪ‬	.	‫داﺷﺖ‬ ‫را‬	(	‫درﺻﺪ‬

‫ﺷﺎﻫﺪ‬ ‫ﺗﯿﻤﺎر‬ ‫در‬ ‫ﻣﺸﻬﺪي‬ ‫ﺗﻮده‬ ‫ﺑﻪ‬ ‫ﻣﺘﻌﻠﻖ‬ ‫ﻣﻌﻨﯽ‬ ‫ﺗﻔﺎوت‬ ‫ﺗﻮده‬ ‫ﺑﺎ‬ ‫داري‬ ‫ﻧﯽ‬ ‫ﻫﻨﺪي،‬ ‫ﻫﺎي‬ ‫ﻧﺪاد‬ ‫ﻧﺸﺎن‬ ‫اﺻﻔﻬﺎﻧﯽ‬ ‫و‬ ‫رﯾﺰي‬ . ‫ﺗﻮده‬ ‫در‬ ‫اردﺳ‬ ‫ﻫﺎي‬ ‫ﻧﯽ‬ ‫و‬ ‫ﻣﺸﻬﺪي‬ ‫ﺘﺎﻧﯽ،‬ ‫ﺷﻮري‬ ‫اﻓﺰاﯾﺶ‬ ‫ﺑﺎ‬ ‫رﯾﺰي،‬ ‫ﻃﻮر‬ ‫ﺑﻪ‬ ‫ﮔﯿﺎﻫﭽﻪ‬ ‫ﻃﻮل‬ ‫ﻣﻌﻨﯽ‬ ‫داري‬ ‫ﺷﻮري‬ ‫ﺳﻄﻮح‬ ‫ﺑﯿﻦ‬ ‫اﺻﻔﻬﺎﻧﯽ‬ ‫ﺗﻮده‬ ‫در‬ ‫ﮐﺎﻫﺶ‬ ‫اﯾﻦ‬ ‫وﻟﯽ‬ ‫ﯾﺎﻓﺖ،‬ ‫ﮐﺎﻫﺶ‬ 3 ‫و‬ dS/m 6 ‫ﻧﯿﺰ‬ ‫و‬ 12 ‫و‬ dS/m 15 ‫ﻣﻌﻨﯽ‬ ‫ﻧﺒﻮد‬ ‫دار‬ . ‫در‬ ‫ﮔﯿﺎﻫﭽﻪ‬ ‫ﻃﻮل‬ ‫ﻫﻨﺪي،‬ ‫ﺗﻮده‬ ‫در‬ dS/m 3 ‫ﺷﻮري‬ ‫وﻟﯽ‬ ‫ﺑﻮد،‬ ‫ﻣﺸﺎﺑﻪ‬ ‫ﺷﺎﻫﺪ‬ ‫ﺑﺎ‬ ‫ﻣﻌﻨﯽ‬ ‫ﮐﺎﻫﺶ‬ ‫ﻣﻮﺟﺐ‬ ‫ﺑﺎﻻﺗﺮ‬ ‫ﻫﺎي‬ ‫دا‬ ‫ﮔﺮدﯾﺪ‬ ‫آن‬ ‫ر‬ . ‫ﮔﯿﺎﻫﭽﻪ‬ ‫ﺑﻨﯿﻪ‬ ‫ﺷﺎﺧﺺ‬ ‫ﺑﯿﺸﺘﺮﯾﻦ‬ ) 44 / 20 ( ‫ﺗﻮده‬ ‫ﺑﻪ‬ ‫ﻣﺘﻌﻠﻖ‬ ‫ﻧﯽ‬ ‫و‬ ‫ﻣﺸﻬﺪي‬ ‫ﻫﺎي‬ ‫در‬ ‫اردﺳﺘﺎﻧﯽ‬ ‫ﺗﻮده‬ ‫و‬ ‫ﺑﻮد‬ ‫ﺷﺎﻫﺪ‬ ‫ﺗﯿﻤﺎر‬ ‫در‬ ‫رﯾﺰي‬ dS/m 18

  
	‫ﺷﻮري‬ ‫ﺳﻄﺢ‬	.	‫ﺑﻮد‬ ‫دارا‬ ‫را‬	(	/ 0	) 39	‫ﻣﻘﺪار‬ ‫ﮐﻤﺘﺮﯾﻦ‬

‫ﺗﺎ‬ ‫اﺑﺘﺪا‬ ‫ﮔﯿﺎﻫﭽﻪ‬ ‫ﺧﺸﮏ‬ ‫وزن‬ ‫ﮐﻪ‬ ‫داد‬ ‫ﻧﺸﺎن‬ ‫ﻧﺘﺎﯾﺞ‬ dS/m 3 ‫ﺑﺪون‬ ‫ﺗﻐﯿﯿﺮ‬ ‫ﺑﻮد‬ ‫ﺑﺎ‬ ‫ﺳﭙﺲ‬ ‫و‬ ‫ﺗﺪ‬ ‫ﺑﻪ‬ ‫ﺷﻮري‬ ‫اﻓﺰاﯾﺶ‬ ‫ﯾﺎﻓﺖ‬ ‫ﮐﺎﻫﺶ‬ ‫رﯾﺞ‬ . ‫ﺗﻮده‬ ‫در‬ ‫ﻧﯽ‬ ‫و‬ ‫ﻫﻨﺪي‬ ‫ﻫﺎي‬ ‫ﺷﻮري‬ ‫رﯾﺰي،‬ ‫از‬ ‫ﺑﺎﻻﺗﺮ‬ ‫ﻫﺎي‬ dS/m 6 ‫ﺗﺪرﯾﺞ‬ ‫ﺑﻪ‬ ‫را‬ ‫ﮔﯿﺎﻫﭽﻪ‬ ‫ﺧﺸﮏ‬ ‫وزن‬ ، ‫دادﻧﺪ‬ ‫ﮐﺎﻫﺶ‬ . ‫ﺗﻮده‬ ‫ﺑﺮاي‬ ‫ﺷﻨﺒﻠﯿﻠﻪ‬ ‫ﺷﻮري‬ ‫ﺑﻪ‬ ‫ﺗﺤﻤﻞ‬ ‫آﺳﺘﺎﻧﻪ‬ ‫ﺣﺪ‬ ‫ﻧﯽ‬ ‫و‬ ‫ﻣﺸﻬﺪي‬ ‫ﻫﻨﺪي،‬ ‫اﺻﻔﻬﺎﻧﯽ،‬ ‫اردﺳﺘﺎﻧﯽ،‬ ‫ﻫﺎي‬ ‫ﺗﺮﺗﯿﺐ،‬ ‫ﺑﻪ‬ ‫رﯾﺰي‬ 69

  
	4 ،	/																	
	‫ﮐﺎﻫﺶ‬ ‫ﺷﯿﺐ‬ ‫و‬	7 (	83 /	) dS/m	‫ﺷﻮري‬ ‫ﺑﻪ‬ ‫ﺗﺤﻤﻞ‬ ‫آﺳﺘﺎﻧﻪ‬ ‫ﺣﺪ‬ ‫ﺑﯿﺸﺘﺮﯾﻦ‬ ‫ﺗﺮﺗﯿﺐ،‬	‫اﯾﻦ‬ ‫ﺑﻪ‬	.	‫آﻣﺪ‬ ‫ﺑﺪﺳﺖ‬	dS/m	1	/	57	‫و‬	1	69 /	،	83 / 7	4 ،	90 /
	‫ﺣﺎﺻﻞ‬	‫درﺻﺪ‬ (	/ 4	63	‫و‬	1	57 /	dS/m	‫ﺗﺮﺗﯿﺐ‬ ‫ﺑﻪ‬	)	‫ﻧﯽ‬ ‫ﺗﻮده‬ ‫از‬ ‫آن‬ ‫ﻣﻘﺪار‬ ‫ﮐﻤﺘﺮﯾﻦ‬ ‫و‬ ‫رﯾﺰي‬	‫ﻫﻨﺪي‬ ‫ﺗﻮده‬ ‫از‬	(	‫درﺻﺪ‬	) 55 / 7	‫ﺷﺪن‬ ‫ﺳﺒﺰ‬ ‫درﺻﺪ‬

‫ﮔﺮدﯾﺪ‬ . ‫ﻣﺪل‬ ‫ﻧﺘﺎﯾﺞ‬ ‫ﻏﯿﺮ‬ ‫ﻫﺎي‬ ‫ﮔﯿﺎﻫﭽﻪ‬ ‫آن‬ ‫در‬ ‫ﮐﻪ‬ ‫ﺷﻮري‬ ‫ﺑﯿﺸﺘﺮﯾﻦ‬ ‫ﮐﻪ‬ ‫داد‬ ‫ﻧﺸﺎن‬ ‫ﺧﻄﯽ‬ ‫ﻣﻘﺪار‬ ‫ﺑﻪ‬ ‫ﻫﺎ‬ 50 ‫د‬ ‫ﺟﻮاﻧﻪ‬ ‫رﺻﺪ‬ ‫زدﻧﺪ‬ ) dS/m 24 / 14 ( ‫از‬ ‫ﻫﻨﺪي‬ ‫ﺗﻮده‬ ‫ﮔﺮدﯾﺪ‬ ‫ﺣﺎﺻﻞ‬ . ‫ﻧﺘﯿﺠﻪ‬ ‫ﮔﯿﺮي‬ : ‫ﺗﻮده‬ ‫ﺷﻮري‬ ‫ﺑﻪ‬ ‫ﺗﺤﻤﻞ‬ ‫ﺷﺎﺧﺺ‬ ‫ﻣﻘﺎﯾﺴﻪ‬ ‫ﻧﺘﺎﯾﺞ،‬ ‫اﺳﺎس‬ ‫ﺑﺮ‬ ‫ﻣﺪل‬ ‫ارزﯾﺎﺑﯽ‬ ‫ﻧﯿﺰ‬ ‫و‬ ‫ﺷﻨﺒﻠﯿﻠﻪ‬ ‫ﻫﺎي‬ ‫ﮐﻪ‬ ‫داد‬ ‫ﻧﺸﺎن‬ ‫ﺗﺠﺮﺑﯽ‬ ‫ﻫﺎي‬ ‫ﺗﻮده‬ ‫ﻣﺮﺣﻠﻪ‬ ‫در‬ ‫ﻫﻨﺪي‬ ‫ﻣﯽ‬ ‫ﺷﺪن‬ ‫ﺳﺒﺰ‬ ‫ﻣﺘﺤﻤﻞ‬ ‫ﻋﻨﻮان‬ ‫ﺑﻪ‬ ‫ﺗﻮاﻧﺪ‬ ‫ﺗﺮﯾﻦ‬ ‫ﺗﻮده‬ ‫ﺑﻬﺮه‬ ‫ﺑﺮاي‬ ‫ﺷﻮري‬ ‫ﺑﻪ‬ ‫ﻣﻨﺎﺑﻊ‬ ‫از‬ ‫ﺑﺮداري‬ ‫ﮔﺮدد‬ ‫ﻣﻌﺮﻓﯽ‬ ‫ﺷﻮر‬ ‫ﺧﺎك‬ ‫و‬ ‫آب‬ . ‫واژه‬ ‫ﮐﻠﯿﺪي‬ ‫ﻫﺎي‬ : ‫ﺳﯿﮕﻤﻮﺋﯿﺪي‬ ‫ﻣﺪل‬ ‫ﺧﻄﯽ،‬ ‫ﻣﺪل‬ ‫ﮔﯿﺎﻫﭽﻪ،‬ ‫ﺑﻘﻮﻻت،‬ ‫ﺟﻨﺒﻪ‬ ‫ﻧﻮآوري‬ ‫ﻫﺎي‬ :

  
			...	‫ﯿ‬ ‫ﻠﻪ‬	‫ﺷﻨﺒﻠ‬	‫ﻫﺎ‬ ‫ي‬	1400 ‫ﯽ‬ ‫ﺗﻮده‬	‫اﯾﺮان‬ / ‫ﺑﻪ‬ ‫ﺗﺤﻤﻞ‬ ‫آﺳﺘﺎﻧﻪ‬ ‫ﺣﺪ‬ ‫ﺳﺎل‬ ‫ﻫﺸﺘﻢ‬ / ‫ﺷﻤﺎره‬ ‫ﺷﻮر‬ ‫ي‬ ‫دوم‬ / ‫ﺑﺮﺧ‬	‫ﺑﺬر‬ ‫ﯿﯿ‬ ‫ﻦ‬	‫ﭘﮋوﻫﺶ‬ : ‫ﻫﻤﮑﺎران‬ ‫و‬ ‫ﺑﻨﺎﮐﺎر‬ ‫ارز‬ ‫ﯾ‬ ‫ﺎﺑ‬ ‫ﯽ‬ ‫ﻫﺎي‬ ‫ﺗﻌ‬ ‫و‬
	‫ﺑﻨﯿﻪ‬ ‫ﺷﺎﺧﺺ‬ ‫روش‬ ‫و‬ ‫ﻣﻮاد‬ ‫ﻫﺎ‬ ‫ﮔﯿﺎﻫﭽﻪ‬ ‫در‬ ‫ﺷﺪه‬ ‫اراﺋﻪ‬ ‫ﻗﺴﻤﺘﯽ‬ ‫ﺳﻪ‬ ‫ﺧﻄﯽ‬ ‫ﻣﻌﺎدﻻت‬ ‫اﺳﺎس‬ ‫ﺑﺮ‬ ‫ﮔﯿﺎﻫﭽﻪ‬ ‫ﻃﻮل‬ ‫و‬ ‫ﮔﺮدﯾﺪ‬ ) ‫روﻣﺎﻧ‬ ‫و‬ ‫ﯽ‬	‫ﻫﺎﻓﻤﻦ‬ ‫و‬ ‫واﻧﮕﻨﻮﺧﺘﻦ‬ ‫ﺗﻮده‬ ‫ﺷﻮري،‬ ‫ﺗﻨﺶ‬ ‫ﺑﻪ‬ ‫ﺗﺤﻤﻞ‬ ‫ﺷﺎﺧﺺ‬ 1 ) 1984 ( ، ‫ﺑﻪ‬ ‫ﻣﺘﺤﻤﻞ‬ ‫ﺑﺮﺗﺮ‬ ‫ﻫﺎي‬ ‫ﻏ‬ ‫ﻣﺪل‬ ‫ﯿ‬ ‫ﺮ‬ ‫ﺧﻄ‬ ‫ﯽ‬
	‫اﺣﺘﺸﺎﻣﯽ‬ ‫ﺗﻮده‬ ‫ﭘﻨﺞ‬ ‫ﺑﺬرﻫﺎي‬ 9 ، 2004 .( ‫ﺣﺴﯿﻦ‬ ‫و‬ ‫زﻫﯿﺮ‬ ‫ﺷﻨﺒﻠﯿﻠﻪ‬ ‫اردﺳﺘﺎﻧﯽ،‬ ‫ﻫﻨﺪي،‬ ‫ﺷﺎﻣﻞ‬ 10 ) 2011 ( ، ‫ﮐﺎﻫﺶ‬ ‫ﺟﺪول‬ 3 ‫ﺷﺪن‬ ‫ﺳﺒﺰ‬ ‫ﮐﺎﻫﺶ‬ ‫ﺷﯿﺐ‬ ‫ﺑﺎﻻﺗﺮﯾﻦ‬ ، ‫از‬ ‫ﺗﻮده‬ ‫ﻫﺎ‬ ‫ي‬	‫ﻣﻄﺮح‬ ‫را‬ ‫ﺷﻮري‬ ‫ﺑﻪ‬ ‫ﮔﯿﺎﻫﺎن‬ ‫ﻋﻤﻠﮑﺮد‬ ‫واﮐﻨﺶ‬ ‫ﮔﺮدﯾﺪﻧﺪ‬ ‫ﻣﺸﺨﺺ‬ ‫ﺷﺪن‬ ‫ﺳﺒﺰ‬ ‫ﻣﺮﺣﻠﻪ‬ ‫در‬ ‫ﺷﻨﺒﻠﯿﻠﻪ‬ ‫ﺷﻮري‬ ‫ﮐﺮده‬ ‫ﻧﺸﺎن‬ ‫و‬ .
	‫ﺟﻮاﻧﻪ‬ ‫ﻧﯽ‬ ‫اﺻﻔﻬﺎﻧﯽ،‬ ‫زﻧﯽ‬ ‫ﺷﻨﺒﻠﯿﻠﻪ‬ ‫در‬ ‫را‬ ‫ﻣﺸﻬﺪي‬ ‫و‬ ‫رﯾﺰي‬ ‫اﺻﻔﻬﺎﻧﯽ‬ ‫و‬ ‫ﻫﻨﺪي‬ ) ‫ﺗﺮﺗﯿﺐ‬ ‫ﺑﻪ‬ ‫ﺑﻪ‬ ) ‫ﺗﻬﯿ‬ 62 ‫ﭘﺎﮐﺎن‬ ‫ﺷﺮﮐﺖ‬ ‫از‬ ‫ﺷﺪه‬ ‫ﻪ‬ ‫ﺷﻮري‬ ‫در‬ ‫درﺻﺪ‬ 55 / 7 ‫و‬ 25 / 7 ‫درﺻﺪ‬ ( ‫و‬	‫ﺻﻮرت‬ ‫ﺑﻪ‬	‫ﮔ‬ ‫ﻨﺶ‬ ‫ﯿ‬ ‫ﺷﻮر‬ ‫ﺑﻪ‬ ‫ﺎﻫﺎن‬ ‫ي‬	‫ﮐ‬ ‫وا‬ ‫ﻪ‬ ‫ﮐ‬	‫دادﻧﺪ‬
	dS/m 15 ‫ﺳﺎل‬ ‫در‬ ‫اﺻﻔﻬﺎن‬ ‫ﺑﺬر‬ ‫ﮐﺮدﻧﺪ‬ ‫ﮔﺰارش‬ 1397 . ( ‫وﯾﻤﺎﻻ‬ ‫و‬ ‫ﺷﺮﻣﺎ‬ ‫ﻣﺮﮐﺰ‬ ‫ﺗﺤﻘﯿﻘﺎﺗﯽ‬ ‫ﮔﻠﺨﺎﻧﻪ‬ ‫در‬ 11 ) 2016 ( ، ‫ﭘﺎﯾﯿﻦ‬ ‫ﺷﯿﺐ‬ ‫ﻣﻘﺪار‬ ‫ﺗﺮﯾﻦ‬ ) 63 / 4 ‫درﺻﺪ‬ ( ‫ﻧﯽ‬ ‫ﺗﻮده‬ ‫از‬ ‫رﯾﺰي‬	‫ﻫﺮ‬ ‫اﻓﺰاﯾﺶ‬ ‫ﺑﺎ‬	‫ﻣﺪل‬ ‫اﯾﻦ‬ ‫س‬ ،	‫اﺳﺎ‬ ‫ﺑﺮ‬	‫ﻣﯽ‬ ‫ﺑﺎﺷﺪ‬ .	‫ي‬	‫ﯿ‬ ‫ﺪ‬	‫ﺳ‬ ‫ﻧﺘﺎﯾﺞ‬ ‫ﯿ‬ ‫ﮕﻤﻮﺋ‬
	‫ﺟﻮاﻧﻪ‬ ‫ﮔﺮﻓﺘﻨﺪ‬ ‫ﻗﺮار‬ ‫ﻣﻄﺎﻟﻌﻪ‬ ‫ﻣﻮرد‬ ‫ﺷﻮري‬ ‫ﺗﺤﻘﯿﻘﺎت‬ ‫ﻣﻠﯽ‬ ‫زﻧﯽ‬ ‫رﺷﺪ‬ ‫و‬ ‫ﮔﯿﺎﻫﭽﻪ‬ ‫ﻫﺎ‬ ‫ﺗﻨﺶ‬ ‫ﺗﺤﺖ‬ ‫ﺷﻨﺒﻠﯿﻠﻪ‬ ‫در‬ ‫را‬ . ‫ﺑﺬرﻫﺎ‬ ‫ﮔﺮدﯾﺪ‬ ‫ﺣﺎﺻﻞ‬ . ‫ﻣﺪل‬ ‫ﺳﺎﯾﺮ‬ ‫ﺟﺪول‬ ‫در‬ ‫ﺷﺪه‬ ‫اراﺋﻪ‬ ‫ﻫﺎي‬ 3 ،	‫ﻧﺴﺒﯽ‬ ‫ﻋﻤﻠﮑﺮد‬ ‫ﻣﯿﺰان‬ ‫ﺷﻮري،‬ ‫ﺳﻄﺢ‬ ‫ﮐﻪ‬ ‫داد‬ ‫ﻧﺸﺎن‬ ‫ﻧﺘﺎﯾﺞ‬ ‫ﺗﻮده‬ ‫اﺻﻠﯽ‬ ‫اﺛﺮ‬ ‫و‬ ‫ﺷﻮري‬ ‫اﺻﻠﯽ‬ ‫اﺛﺮ‬ ‫اﺑﺘﺪا‬ ‫ﻫﻤﺎن‬ ‫از‬ ‫ﺑﻪ‬
	‫ﻣﻄﺎﻟ‬ ‫ﺷﻮري‬ ‫ﺿﺪﻋﻔﻮﻧﯽ‬ ‫از‬ ‫ﭘﺲ‬ ‫ﻌ‬ ‫ﮐﻪ‬ ‫دادﻧﺪ‬ ‫ﻧﺸﺎن‬ ‫و‬ ‫ﮐﺮده‬ ‫ﻪ‬ ‫داﺧﻞ‬ ‫ﮔﻠﺪان‬ ‫ﻫﺎي‬ ‫اﺑﻌﺎد‬ ‫ﺑﻪ‬ ‫ﭘﻼﺳﺘﯿﮑﯽ‬ ‫ﺗﻤﺎم‬ ‫ﺗﺎ‬ ‫ﺑﺬرﻫﺎ‬ ‫ﺗﻮده‬ ‫ﺷﻮري‬ ‫ﺑﻪ‬ ‫واﮐﻨﺶ‬ ‫را‬ ‫ﺷﻮري‬ ‫ﺑﻪ‬ ‫ﺷﻨﺒﻠﯿﻠﻪ‬ ‫ﻣﺨﺘﻠﻒ‬ ‫ﻫﺎي‬	‫ﮐﺮده‬ ‫ﺳ‬ ‫در‬ ‫در‬ ‫و‬ ‫درﺻﺪ‬ ‫ﯾﮏ‬ ‫ﻄﺢ‬ ‫ﻧﻘﻄﻪ‬ EC 50	‫ﻏﯿﺮ‬ ‫ﺻﻮرت‬ ‫ﺑﺮ‬ ‫ﺻﻔﺎت‬ ‫ﺗﻤﺎم‬ ‫ﮐﺎﻫﺶ‬ ‫ﺑﻪ‬ ‫ﺷﺮوع‬ ‫ﺧﻄﯽ‬ ‫اﻧﺪازه‬ ‫ﻣﻮرد‬ ‫ﮔﯿﺮي‬
	‫ﺷﻮري‬ ‫ﻫﺎي‬ ‫ﻣﺤﯿﻂ‬ ‫در‬	‫ﺷﻮري‬ 15 × 12 mM NaCl 100 ‫ﺳﺎﻧﺘﯽ‬ ‫ﻣﺘﺮ‬ ‫ﻋﻤﻖ‬ ‫در‬ ‫زده‬ ‫ﺟﻮاﻧﻪ‬ 5 / 1 ‫ﺳﺎﻧﺘﯽ‬ ، ‫ا‬ ‫در‬ ‫ﻣﺎ‬ ‫ﻣﺘﺮي‬ ‫ﭘﯿﺶ‬ ‫ﻏﯿﺮﺧﻄﯽ‬ ‫ﺻﻮرت‬ ‫ﺑﻪ‬ ‫ﻣﯽ‬ ‫ﺑﯿﻨﯽ‬ ‫ﮐﻨﻨﺪ‬ .	، ‫ﺑﻪ‬ ‫ﺑﻮد‬ ‫دار‬ ‫آن‬ ‫ﻣﻘﺪار‬ 50 2002 ‫درﺻﺪ‬ .( ‫ﻣﻌﻨﯽ‬ ) ‫ﺟﺪول‬ 2 ‫ﻣﻬﻤﯽ‬ ‫داروﯾﯽ‬ ‫ﺧﻮاص‬ ‫ﺗﺮﯾﮕﻮﻧﻠﯿﻦ‬ ‫ﻣﯽ‬ ‫ﮐﺎﻫﺶ‬ ‫ﯾﺎﺑﺪ‬ ) ‫راﺑﻄﻪ‬ 2 .( .( ‫ﻫﻤﭽﻨﯿﻦ،‬ ‫ﺑﺮﻫﻢ‬ ‫ﮐﻨﺶ‬ ‫ﺷﻮري‬ ‫و‬
	‫ﻣﯿﺰان‬ ‫ﺑﺎﻻﺗﺮ‬ ‫ﮔﺮﻓﺘﻨﺪ‬ ‫ﻗﺮار‬ ‫ﺷﻦ‬ ‫ﺟﻮاﻧﻪ‬ . ‫ﻣﺪل‬ ‫در‬ ‫ﺷﻮري‬ ‫ﺳﻄﺢ‬ ‫ﻫﺮ‬ ‫اﻓﺰاﯾﺶ‬ ‫ﺑﺎ‬ ‫ﻏﯿﺮﺧﻄﯽ‬ ‫ﻫﺎي‬ ‫زﻧﯽ‬ ‫ﯾﺎﻓﺖ‬ ‫ﮐﺎﻫﺶ‬ ‫ﺷﺪت‬ ‫ﺑﻪ‬ ، ‫در‬ ‫ﺑﻄﻮرﯾﮑﻪ‬ ‫آ‬ ‫اﻧﺠﺎم‬ ‫ﻣﻨﻈﻮر‬ ‫ﺑﻪ‬ ‫ﺑﺸﻮﯾﯽ‬ ‫ﻣﺆﺛﺮ‬ ، ‫ﮔﻠﺪ‬ ‫ان‬ ‫ﻫﺎ‬	‫ﻧ‬ ‫ﺿﺪﻋﻔﻮﻧﯽ‬ ‫ﻣﯿﮕﺮن،‬ ‫ﺿﺪ‬ ‫ﺳﺮﻃﺎن،‬ ‫ﺿﺪ‬ ‫ﻈﯿﺮ‬ ‫ﭘﺎﯾﯿﻦ‬ ‫ﮐﻨﻨﺪﮔﯽ،‬ ) ‫راﺑﻄﻪ‬ 2 ( ] Y = Y m /[(1+ (EC / EC 50 ) p ‫درﺻﺪ‬ ‫ﯾﮏ‬ ‫ﺳﻄﺢ‬ ‫در‬ ‫ﻣﻄﺎﻟﻌﻪ‬ ‫ﻣﻮرد‬ ‫ﺻﻔﺎت‬ ‫ﺑﺮاي‬ ‫ﻧﯿﺰ‬ ‫ﺗﻮده‬
	‫ﺷﻮري‬ ‫ﺷﺪن‬ ‫ﺳﻮراخ‬ ‫از‬ ‫ﭘﺲ‬ mM 200 ‫ﺟﻮاﻧﻪ‬ ‫زﻧ‬ ‫ﺷ‬ ‫ﺑﺎ‬ ‫اﺑﺘﺪا‬ ‫ﯽ‬ 60 ‫ﺷﻦ‬ ‫ﺑﺎ‬ ‫ﺳﭙﺲ‬ ‫و‬ ‫درﺷﺖ‬ ‫ﻦ‬ ‫درﺻﺪ‬ ‫ﮐﺮد‬ ‫ﭘﯿﺪا‬ ‫ﮐﺎﻫﺶ‬ . ‫ﺗﺪرﯾﺠ‬ ‫ﻃﻮر‬ ‫ﺑﻪ‬ ‫ﺷﺪن‬ ‫ﺳﺒﺰ‬ ‫ﻣﯿﺰان‬ ‫ﺑﻪ‬ ‫ﺷﺮوع‬ ‫اﺑﺘﺪا‬ ‫ﻫﻤﺎن‬ ‫از‬ ‫ﯽ‬	‫دارا‬ ‫را‬ ‫دﯾﺎﺑﺖ‬ ‫ﺿﺪ‬ ‫و‬ ‫ﺧﻮن‬ ‫ﭼﺮﺑﯽ‬ ‫آورﻧﺪه‬ ‫راﺑﻄﻪ،‬ ‫اﯾﻦ‬ ‫در‬ Y m ‫ﺷﺮاﯾﻂ‬ ‫در‬ ‫ﻋﻤﻠﮑﺮد‬ ‫ﺣﺪاﮐﺜﺮ‬ ‫ﻣﯽ‬ ‫ﺑﺎﺷﺪ‬ . ‫ﭘﺰﺷﮑﺎن‬ ‫ﻣﻌﻨﯽ‬ ‫ﮔﺮدﯾﺪ‬ ‫دار‬ ) ‫ﺟﺪول‬ 2 .(
	‫ﻫﻤﭽﻨ‬ ‫رﺷﺪ‬ ‫ﮐﺎﻫﺶ‬ ‫ﻣﻮﺟﺐ‬ ‫ﺷﻮري‬ ‫ﺗﻨﺶ‬ ‫ﯿﻦ،‬ ‫ﺷﺪﻧﺪ‬ ‫ﭘﺮ‬ ‫رﯾﺰ‬ . ‫ﺗ‬ ‫ﯿ‬ ‫ﻤﺎر‬ ‫ﺷﺎﻣﻞ‬ ‫ﺷﻮري‬ ‫ﻫﻔﺖ‬ ‫ﺳﻄﺢ‬ ‫ﮔﯿﺎﻫﭽﻪ‬ ) dS/m ‫ﻫﺎ‬ ‫و‬ ‫ﻣﯽ‬ ‫ﯾﺎﻓﺘﻦ‬ ‫ﮐﺎﻫﺶ‬ ‫ﮐﻨﺪ‬ ) ‫ﺷﮑﻞ‬ 1 .( ‫ﺗﻮده‬ ‫ﻣﻘﺎﯾﺴﻪ‬ ‫ﻫﺎي‬	‫زﻣﺎن‬ ‫از‬ ‫ﻋﺮب‬ ‫و‬ ‫اﯾﺮاﻧﯽ‬ ‫ﻏﯿﺮﺷﻮر‬ ، EC 50 ‫اﻧﺪازه‬ ‫ﺑﻪ‬ ‫ﻋﻤﻠﮑﺮد‬ ‫آن‬ ‫در‬ ‫ﮐﻪ‬ ‫ﺷﻮري‬ ‫ﻫﺎ‬ ‫ﺑﺮاي‬ ‫ﺷﻨﺒﻠﯿﻠﻪ‬ ‫داﻧﻪ‬ ‫از‬ ‫ﻗﺪﯾﻢ‬ ‫ي‬ 50 ‫آﺳﺘﺎﻧﻪ‬ ‫ﺣﺪ‬ ‫ﻣﻘﺪار‬ ‫ﺑﺎﻻﺗﺮﯾﻦ‬ ‫ﺧﻄﯽ‬ ‫ﻣﺪل‬ ‫اﺳﺎس‬ ‫ﺑﺮ‬
	‫ﺗﺄﺧ‬ ‫ﯿ‬ ‫ﺮ‬ ‫ﮐﻪ‬ ‫دادﻧﺪ‬ ‫ﻧﺸﺎن‬ ‫ﺟﻮاﻧﻪ‬ ‫زﻧﯽ‬ 5 / 0 3 ، 6 ، 9 ، ‫ﻣﺪل‬ ‫اﺳﺎس‬ ‫ﺑﺮ‬ ‫ﮐﻪ‬ ‫داد‬ ‫ﻧﺸﺎن‬ ‫ﯾﮑﺪﯾﮕﺮ‬ ‫ﺑﺎ‬ ‫ﺷﻨﺒﻠﯿﻠﻪ‬ ‫ﻣﺨﺘﻠﻒ‬ ‫ﮔﺮدﯾﺪ‬ . ‫ﭼﻮدﻫﻮري‬ 12 ‫ﻫﻤﮑﺎران‬ ‫و‬ ) 2014 ( ‫ﻣﺮﺣﻠﻪ‬ ‫در‬ ‫ﺟﻮاﻧﻪ‬ ‫زﻧﯽ‬ ‫ﺷﻮري‬ ‫ﮐﻪ‬ ‫ﻫﻨﮕﺎﻣﯽ‬ 12 ، 15 ‫و‬ 18 ( ‫ﻣﺨﻠﻮط‬ ‫ﻃﺮﯾﻖ‬ ‫از‬ ‫ﮐﻪ‬ ‫ﺑﻮد‬ ، ‫آب‬ ‫ﮐﺮدن‬ ‫ﺷﺮب‬ ) ‫اﻟﮑﺘﺮﯾﮑﯽ‬ ‫ﻫﺪاﯾﺖ‬ ‫ﺑﺎ‬ dS/cm 375 / 0 ( ‫و‬ ‫ﮔﯿﺎﻫﭽﻪ‬ ‫آن‬ ‫در‬ ‫ﮐﻪ‬ ‫ﺷﻮري‬ ‫ﺑﯿﺸﺘﺮﯾﻦ‬ ‫ﺳﯿﮕﻤﻮﺋﯿﺪي،‬ ‫ﺑﻪ‬ ‫ﻫﺎ‬	‫زﯾ‬ ‫اﺳﺘﻔﺎده‬ ‫ﻗﻨﺪ‬ ‫ﺑﯿﻤﺎري‬ ‫ﻣﺪاواي‬ ‫ﺑﻌﻤﻞ‬ ‫ﺎد‬ ) ‫ﻣﻬﺮآﻓﺮﯾﻦ‬ 5 ‫ﻫﻤﮑﺎران،‬ ‫و‬ 2011 ‫ﺗﺴﯽ‬ ‫؛‬ 6 ‫ﻫﻤﮑﺎران،‬ ‫و‬ ‫ﻣﯽ‬ ‫آوردﻧﺪ‬ ‫ﻣﯽ‬ ‫ﮐﺎﻫﺶ‬ ‫درﺻﺪ‬ ‫و‬ ‫ﯾﺎﺑﺪ‬ p ‫اﺳﺖ‬ ‫ﺗﺠﺮﺑﯽ‬ ‫ﺛﺎﺑﺖ‬ ‫ﯾﮏ‬ . ‫اﺳﺘﻔﺎن‬ ) dS/m 83 / 7 ( ‫ﺗﻮده‬ ‫ﺳﭙﺲ‬ ‫و‬ ‫ﻫﻨﺪي‬ ‫ﺗﻮده‬ ‫ﺑﻪ‬ ‫ﻣﺘﻌﻠﻖ‬ ‫ﻫﺎي‬ 2 ‫و‬ ‫ﻫﻤﮑﺎران‬ ) a 2005 ( ‫ﺑﺎ‬ ‫راﺑﻄﻪ‬ ‫ﺟﺰﺋﯽ‬ ‫ﭼﻨﺪ‬ ‫اردﺳﺘﺎﻧﯽ‬ ‫و‬ ‫اﺻﻔﻬﺎﻧﯽ‬ ) ‫ﺗﺮﺗﯿﺐ‬ ‫ﺑﻪ‬ 90 / 4 ‫و‬ dS/m 69 / 4 (
	‫ا‬ ‫ﺧﺎك‬ ‫آب‬ ‫ﺑﺴﯿﺎر‬ ‫ز‬ dS/m 4 ‫ﻃﺒﯿﻌﯽ‬ ‫ﺷﻮر‬ ‫ﺗﻠﻔﺎت‬ ‫ﻣﯿﺰان‬ ‫رﻓﺖ‬ ‫ﺑﺎﻻﺗﺮ‬ ) ‫اﻟﮑﺘﺮﯾﮑﯽ‬ ‫ﻫﺪاﯾﺖ‬ ‫ﺑﺎ‬ ‫ﮔﯿﺎﻫﭽﻪ‬ ‫ﺣﺪود‬ ‫ﻫﺎ‬ ‫ي‬ ‫ﻣﻘﺪار‬ 50 ‫درﺻﺪ‬ ‫ﺷﺪﻧﺪ‬ ‫ﺳﺒﺰ‬ ) EC 50 ( ‫ﻫﻨﺪي‬ ‫ﺗﻮده‬ ‫از‬	2016 .( ‫ﯾﺎﻓﺘﻪ‬ ‫ﺗﻐﯿﯿﺮ‬ ‫ﻧﺰوﻟﯽ‬ ‫ﺑﻮد‬ . ‫ﭘﺎﯾﯿﻦ‬ ‫ﻫﻤﭽﻨﯿﻦ،‬ ‫راﺑﻄﻪ‬ ‫ﺑﻪ‬ ‫ﺗﺤﻤﻞ‬ ‫آﺳﺘﺎﻧﻪ‬ ‫ﺣﺪ‬ ‫ﻣﻘﺪار‬ ‫ﺗﺮﯾﻦ‬ ‫ﺻﻮرت‬ ‫ﺑﻪ‬ ‫را‬ ‫دﯾﮕﺮي‬ ‫راﺑﻄﻪ‬ 3
	‫زﯾﺎ‬ ‫ﻣﻘﺪار‬ ‫ﺑﻪ‬ ‫ﺷﻨﺒﻠﯿﻠﻪ‬ ‫دي‬ ‫اﻻدرﯾﺴﯽ‬ ‫ﻣﺼﺒﺎح‬ dS/m 500 ( ‫ﺣﺎﺻﻞ‬ ‫ﮔﺮدﯾﺪ‬ ) dS/m 24 / 14 ( ‫آﻣﺪ‬ ‫ﺑﺪﺳﺖ‬ ‫ﯾﺎﻓﺖ‬ ‫ﮐﺎﻫﺶ‬ . ) ‫ﺟﺪول‬ 1 .( ‫ﻋ‬ ‫ﻤ‬ ‫ﻋ‬ . ‫ﺳﺎﯾﺮ‬ ‫ﺑﺮاي‬ ‫ﺷﻮري‬ ‫اﯾﻦ‬ ‫و‬ ‫ﺒﺪاﻟﻤﻮﻣﻦ‬ ‫آﺑﯿﺎري‬ ‫ﻠﯿﺎت‬ 13 ) 2009 ( ، ‫روي‬ ‫را‬ ‫ﺷﻮري‬ ‫اﺛﺮات‬ ‫ﮔﻠﺪان‬ ‫روزاﻧﻪ‬ ‫ﻫﺎ‬ ‫ﮔﺮﻓﺘﻦ‬ ‫ﻧﻈﺮ‬ ‫در‬ ‫ﺑﺎ‬ 30 ‫آﺑﺸﻮﯾﯽ‬ ‫ﮐﺴﺮ‬ ‫درﺻﺪ‬ ‫ﺗﻮده‬ ‫ﻣﻮ‬ ‫ﻫﺎي‬ ً ‫ﺗﻘﺮﯾﺒﺎ‬ ‫و‬ ‫ﮐﻤﺘﺮ‬ ‫ﻣﻄﺎﻟﻌﻪ‬ ‫رد‬ dS/m 11 ‫ﺑﻮد‬	‫ﺷﻨﺒﻠﯿﻠﻪ‬ ‫اﺳﺖ‬ ‫ﺑﻮده‬ ‫ﺗﻮﺟﻪ‬ ‫ﻣﻮرد‬ ‫ﺷﻮري‬ ‫ﺗﻨﺶ‬ ‫ﺑﻪ‬ ‫ﺗﺤﻤﻞ‬ ‫ﻧﻈﺮ‬ ‫ﺟﻤﻠﻪ‬ ‫از‬ ‫از‬ ‫ﮐﻪ‬ ‫اﺳﺖ‬ ‫داروﯾﯽ‬ ‫ﻣﻔﯿﺪ‬ ‫ﮔﯿﺎﻫﺎن‬ . ‫اﻏﻠﺐ‬ ‫را‬ ‫ﺷﻮري‬ ‫اﻓﺰاﯾﺶ‬ ‫اﺛﺮ‬ ‫در‬ ‫ﻋﻤﻠﮑﺮد‬ ‫ﮐﺎﻫﺶ‬ ‫ﮐﻪ‬ ‫دادﻧﺪ‬ ‫اراﺋﻪ‬ ‫ﺑﺎز‬ ‫ﺗﻮده‬ ‫از‬ ‫ﺷﻮري‬ ‫ﻧﯽ‬ ‫و‬ ‫ﻣﺸﻬﺪي‬ ‫ﻫﺎي‬ ‫رﯾﺰي‬ ) ‫ﺗﺮﺗﯿﺐ‬ ‫ﺑﻪ‬ 69 / 1 ‫و‬ ‫ﺑﻪ‬ ‫ﺻﻮرت‬ ‫ﺳﯿﮕﻤﻮﺋﯿﺪي‬ ‫ﯾﺎ‬ ‫ﺧﻄﯽ‬ ‫ﻏﯿﺮ‬ ‫ﻣﯽ‬ ‫ﻧﺸﺎن‬ ‫دﻫﺪ‬ . ‫در‬ dS/m 57 / 1 ( ‫ﺑ‬ ‫ﻪ‬ ‫آﻣﺪ‬ ‫دﺳﺖ‬ ) ‫ﺟﺪول‬ 3 .(
	‫ﺟﻮاﻧﻪ‬ ‫اﻣﻼح‬ ‫ﺷﺴﺘﺸﻮي‬ ‫ﺑﺮاي‬ ‫زﻧﯽ‬ ‫ﺑﺬر‬ ‫ﺷﻨﺒﻠﯿﻠﻪ‬ ‫در‬ ‫در‬ ‫آﻧﻬﺎ‬ ‫ﺗﺠﻤﻊ‬ ‫از‬ ‫ﺟﻠﻮﮔﯿﺮي‬ ‫و‬ ‫ﮐﻪ‬ ‫دادﻧﺪ‬ ‫ﻧﺸﺎن‬ ‫و‬ ‫ﮐﺮده‬ ‫ﺑﺮرﺳﯽ‬ ) ‫ﺟﺪول‬ 3 .(	‫روي‬	‫ﺷﻮري‬ ‫ﺗﻨﺶ‬	‫اﺛﺮات‬ ‫زﻣﯿﻨﻪ‬	‫در‬	‫ﺷﺪه‬ ‫اﻧﺠﺎم‬	‫ﭘﮋوﻫﺶ‬ ‫ﻫﺎي‬ ‫اﯾﻦ‬ ‫راﺑﻄﻪ‬ ،
	‫ﺗﺄﺛ‬ ‫ﯿ‬ ‫ﺮ‬	‫ﺗﺤﺖ‬	140	mM NaCl	‫ﺟﻮاﻧﻪ‬ ‫رﯾﺸﻪ‬ ‫ﻣﻨﻄﻘﻪ‬ ‫زﻧﯽ‬ ‫ﺷﻮري‬ ‫ﺗﺎ‬ ‫ﺑﺬرﻫﺎ‬ ‫ﮔﺮﻓﺖ‬ ‫اﻧﺠﺎم‬ . ‫ﺷﻬﺮي‬ ‫ﻧﺴﺒﺖ‬ ‫ﺑﻪ‬ 1 ‫ﺑﻪ‬ 20 (	‫ﺷﺮب‬	‫رﺷﺪ‬ ‫ﺷﺪه‬ ‫آب‬ ‫ﺑﺎ‬	‫اوﻟﯿ‬ ‫ﻪ‬ ) ‫رﻗﯿﻖ‬	‫زﻧﯽ‬ ‫اﺳﺘﻔﺎده‬ ‫ﻣﻮرد‬ ‫ﺷﻮر‬ ‫ﯾﺎ‬ ‫و‬ ‫ﻣﺮاﺣﻞ‬	‫اﻏﻠﺐ‬ ‫آب‬ ‫ﺷﯿﻤﯿﺎﯾﯽ‬ ‫ﺗﺠﺰﯾﻪ‬ ‫ﺟﻮاﻧﻪ‬ ‫ﻣﺮﺣﻠﻪ‬ ‫در‬ ‫ﺑﺴﯿﺎر‬	‫ﺷﻨﺒﻠﯿﻠﻪ‬ ، ‫ﺟﺪول‬ 1 .
	‫ﻧﮕﺮﻓﺘﻪ‬ ‫ﻗﺮار‬ ، ‫ﻫﻔﺘﻪ‬ ‫ﺳﻪ‬ ‫دوره‬ ‫ﻃﻮل‬ ‫در‬ ‫اﻣﺎ‬ ‫ﺑﺎﻻﺗﺮ‬ ‫ﺳﻄﻮح‬ ‫ﺗﻌﺪاد‬ ‫اي،‬ ‫ﮐﺎﻫﺶ‬ ‫ﻣﻮﺟﺐ‬ ‫ﺷﻮري‬ ‫ﮔﯿﺎﻫﭽﻪ‬ ‫ﻫﺎ‬ ‫ﺳﺒﺰ‬	‫ﻋﻤﻠﮑﺮد‬ ‫و‬ ‫زاﯾﺸﯽ‬ ‫رﺷﺪ‬ ‫آﻧﻬﺎ‬ ‫از‬ ‫اﻧﺪﮐﯽ‬ ‫ﺗﻌﺪاد‬ ‫و‬ ‫ﺑﻮده‬ (s. EC 50 ) ‫ﻣﯿﺰان‬ ‫ﺑﺮآﻣﺪﮔﯽ‬ ‫ﯾﺎ‬ ‫و‬ ‫ﻓﺮورﻓﺘﮕﯽ‬	‫روﯾﺸﯽ‬
	‫اﯾﻦ‬ ‫در‬	‫ﺷﺪﻧﺪ‬ ‫ﺷﻤﺎرش‬ .	‫ﻣﻌﻨﯽ‬ ‫در‬ ‫روزاﻧﻪ‬ ‫ﺑﻄﻮر‬ ‫ﺷﺪه‬ ‫ﻣﯿﺰان‬ ‫دار‬ ‫ﺟﻮاﻧﻪ‬ ‫زﻧﯽ‬ ‫ﺳﺎﻋﺖ‬ ‫ﮔﺮدﯾﺪ‬ . 13	‫ﮔﯿﺎه‬ ‫ﺑﻪ‬ ‫ﻧﺴﺒﺖ‬ ‫را‬ ‫ﻣﻨﺤﻨﯽ‬ ‫ﻃﺮف‬ ‫دو‬ ‫ﮔﺮﻓﺘﻪ‬ ‫ﺑﺮ‬ ‫در‬ ‫را‬ ‫اﻧﺪ‬ . ‫ﺳﺒﺰ‬ ‫ﻣﺮﺣﻠﻪ‬ ‫ﮐﻪ‬ ‫اﺳﺖ‬ ‫ﺣﺎﻟﯽ‬ ‫در‬ ‫اﯾﻦ‬ EC 50 ‫ﻣﯽ‬ ‫ﻧﺸﺎن‬ ‫دﻫﺪ‬ .
	‫ﻣﺪل‬ ‫ﺷﻮري،‬ ‫ﺑﻪ‬ ‫ﺗﺤﻤﻞ‬ ‫ﻣﻄﺎﻟﻌﺎت‬ ‫در‬ ‫ﻣﺨﺘﻠﻒ‬ ‫ﻫﺎي‬ ‫ﺗﺤﻘﯿﻖ‬ ‫ﺷﺎﺧﺺ‬ ‫ﺑﻨ‬ ‫ﯿ‬ ‫ﻪ‬ ‫ﮔﯿﺎﻫﭽﻪ‬ ‫از‬ ‫ﺣﺎﺻ‬ ‫ﻠﻀﺮب‬ ‫ﺗﻌﺪاد‬	‫ﺟﻮاﻧﻪ‬ ‫ﻣﺮﺣﻠﻪ‬ ‫دﻧﺒﺎل‬ ‫ﺑﻪ‬ ‫ﮐﻪ‬ ‫ﺷﺪن‬ ) ‫راﺑﻄﻪ‬ 3 ( ) Y = 1 / [(1+ (EC / EC 50 ) (s. EC ‫ﺧﺮوج‬ ‫ﺑﻪ‬ ‫و‬ ‫داده‬ ‫رخ‬ ‫زﻧﯽ‬ 50
	‫ﻣﻮرد‬ ‫ﺷﻮري‬ ‫ﺑﻪ‬ ‫ﮔﯿﺎﻫﺎن‬ ‫واﮐﻨﺶ‬ ‫ﺑﺮرﺳﯽ‬ ‫ﺑﺮاي‬ ‫ﺗﺠﺮﺑﯽ‬ ‫ﮔﯿﺎﻫﭽﻪ‬ ‫ﻫﺎ‬ ‫ي‬ ‫ﺳﺒﺰ‬ ‫ﺷﺪه‬ ‫در‬ ‫ﻃﻮل‬ ‫ﮔ‬ ‫ﯿ‬ ‫ﺎﻫﭽﻪ‬ ‫ﻣﺤﺎﺳﺒﻪ‬ ‫ﺷﺪ‬ .	‫ﻣﯽ‬ ‫ﻣﻨﺠﺮ‬ ‫ﺧﺎك‬ ‫از‬ ‫ﮔﯿﺎﻫﭽﻪ‬ ‫ﻋﻮا‬ ‫ﺗﻨﺶ‬ ‫در‬ ‫را‬ ‫زراﻋﯽ‬ ‫ﻣﺤﺼﻮﻻت‬ ‫ﻋﻤﻠﮑﺮد‬ ‫ﻣﺨﺘﻠﻔﯽ‬ ‫ﻣﻞ‬ ‫ﺗﻨﺶ‬ ‫ﻣﻄﺎﻟﻌﺎت‬ ‫در‬ ‫ﮔﺮدد،‬
	‫ﮔﺮﻓﺘﻪ‬ ‫ﻗﺮار‬ ‫اﺳﺘﻔﺎده‬ ‫ﭘﯿﺸﻨﻬﺎدي‬ ‫ﺗﻮﺳﻂ‬ ‫ﻫﺎﻓﻤﻦ‬ ‫و‬ ‫ﻣﺎس‬ ‫اﻧﺪ‬ . ‫ﻣﺪل‬ ‫اﺳﺎس‬ ‫ﺑﺮ‬ ‫ﺻﻮرت‬ ‫ﺑﻪ‬ ‫اﺳﺘﻔﺎده‬ ‫ﻣﻮرد‬ ‫آﻣﺎري‬ ‫ﻃﺮح‬ ‫ﻃﺮح‬ ‫ﺧﻄﯽ‬ ‫ﻗﺴﻤﺘﯽ‬ ‫ﺳﻪ‬ ً ‫ﮐﺎﻣﻼ‬ ‫ﺗﺼﺎدﻓﯽ‬ 14 ) 1977 ( ‫و‬ ‫و‬ ‫واﻟﻨﺪر‬ ‫ﺗﺎﻧﺠﯽ‬ ‫ﺑﻮد‬ ‫ﺗﮑﺮار‬ ‫ﺳﻪ‬ ‫ﺑﺎ‬ ‫ﻓﺎﮐﺘﻮرﯾﻞ‬ ‫آزﻣﺎﯾﺶ‬ ‫ﻗﺎﻟﺐ‬ ‫در‬ . ‫در‬ ‫ﮐﻪ‬ ‫ﺻﻔﺎﺗﯽ‬ 15 ) 2011 ( ‫ﺑﯿﻦ‬ ‫ﺷﻮري‬ ‫ﮐﻪ‬ ‫ﻫﻨﮕﺎﻣﯽ‬ ‫و‬ ‫ﺻﻔﺮ‬ ‫ﺣﺪ‬ ‫اﻧﺪازه‬ ‫ﻣﻮرد‬ ‫ﺗﺤﻘﯿﻖ‬ ‫اﯾﻦ‬ ‫درﺻﺪ‬ ‫ﺷﺎﻣﻞ‬ ‫ﮔﺮﻓﺖ‬ ‫ﻗﺮار‬ ‫ﮔﯿﺮي‬	‫ﺷﻮ‬ ) 2010 ‫اﺳﺖ‬ ‫ﺷﺪه‬ ‫واﻗﻊ‬ ‫ﺗﻮﺟﻪ‬ ‫ﻣﻮرد‬ ‫ﮐﻤﺘﺮ‬ ‫ري‬ ( ، ‫ﺗﺄﺛ‬ ‫ﯿ‬ ‫ﺮ‬ ‫ﺗﻨﺶ‬ ‫اﺳﻤﺰي‬ ) MPa 81 / 0 . -، 37 / 0 -( ‫و‬ ‫ﻧﻮع‬ ‫ﻧﻤ‬ ‫ﮏ‬ ‫را‬ ‫ﺑﺮ‬ ‫ﺟﻮاﻧﻪ‬ ‫زﻧ‬ ‫ﯽ‬ ‫و‬ ‫رﺷﺪ‬ ‫ﮔ‬ ‫ﯿ‬ ‫ﺎﻫﭽﻪ‬ ‫دادﺧﻮاه‬ 59 / 0 -7 ، ‫ﭼﻨﺪ‬ ‫ﺗﺤﺖ‬ ‫ﺷﻮري‬ ‫ﺗﺄﺛ‬ ‫ﯿ‬ ‫ﺮ‬ ‫ﻣﯽ‬ ‫ﻗﺮار‬ ‫و‬ ‫دﻫﻨﺪ‬ ‫ﻟﺬا‬ ‫ﺷﺎﺧﺼﯽ‬ ‫داﺷﺘﻦ‬ ‫ﻣﯽ‬ ‫ﮔﯿﺎﻫﺎن‬ ‫ﺷﻮري‬ ‫ﺑﻪ‬ ‫ﺗﺤﻤﻞ‬ ‫ﻣﻘﺎﯾﺴﻪ‬ ‫ﺑﺮاي‬ ‫ﻣﻔﯿﺪ‬ ‫ﺗﻮاﻧﺪ‬ ‫ﺑﺎﺷﺪ‬ ) ‫ﻫﻤﮑﺎران،‬ ‫و‬ ‫اﺳﺘﻔﺎن‬ a 2005 ‫ﻫﻤﮑﺎران،‬ ‫و‬ ‫اﺳﺘﻔﺎن‬ ‫؛‬
	‫آﺳﺘﺎﻧﻪ‬ ‫ﻧﻤﯽ‬ ‫دﯾﺪه‬ ‫ﻋﻤﻠﮑﺮدي‬ ‫ﮐﺎﻫﺶ‬ ‫ﻫﯿﭽﮕﻮﻧﻪ‬ ‫ﺑﺎﺷﺪ‬ ، ‫ﺑﺮاﺑﺮ‬ ‫ﻧﺴﺒﯽ‬ ‫ﻋﻤﻠﮑﺮد‬ 100 ‫ﺷﻮد‬ ‫و‬ ‫ﺑﻮده‬ ‫درﺻﺪ‬ . ‫اﻣﺎ‬ ، ‫در‬ ‫ﻃﻮل‬ ‫ﺷﺪن،‬ ‫ﺳﺒﺰ‬ ‫ﺳﺮﻋﺖ‬ ‫ﺷﺪن،‬ ‫ﺳﺒﺰ‬ ‫ر‬ ‫ﯾ‬ ‫ﺸﻪ‬ ‫ﺳﺎﻗﻪ،‬ ‫ﻃﻮل‬ ، ‫ﺑﻨﯿﻪ‬ ‫ﺷﺎﺧﺺ‬ ‫ﮔﯿﺎﻫﭽﻪ‬ ‫ﺑﻮد‬ ‫ﮔﯿﺎﻫﭽﻪ‬ ‫ﻃﻮل‬ ‫و‬ ‫ﺧﺸﮏ‬ ‫وزن‬ ، .	‫ﮔ‬ ‫ﺗﺎ‬ ‫آب‬ ‫ﭘﺘﺎﻧﺴﯿﻞ‬ ‫ﮐﺎﻫﺶ‬ ‫ﯿ‬ ‫ﺎه‬ ‫دارو‬ ‫ﯾﯽ‬ ‫ﻣﻄﺎﻟﻌﻪ‬ ‫ﺷﻨﺒﻠﯿﻠﻪ‬ ‫ﺟﻤﻠﻪ‬ ‫از‬ MPa 59 / 0 -b 2005 .( ‫ﻏﯿﺮ‬ ‫ﭘﺎراﻣﺘﺮ‬ ‫اﺳﺎس‬ ‫ﺑﺮ‬ ‫ﺧﻄﯽ‬ EC 50 ‫و‬ ‫ﮐﻪ‬ ‫داد‬ ‫ﻧﺸﺎن‬ ‫ﺗﺄﺛ‬ ‫ﯿ‬ ‫ﺮ‬ ‫ﺑﺮ‬ ‫زﯾﺎدي‬ ‫و‬ s ‫ﺷﺎﺧﺺ‬ ، ‫ﺷﻮري‬ ‫ﺑﻪ‬ ‫ﺗﺤﻤﻞ‬ 3 ‫ﻣﻌﯿﺎر‬ ‫ﻋﻨﻮان‬ ‫ﺑﻪ‬ ‫ﺗﺤﻤﻞ‬ ‫ﻣﻘﺎﯾﺴﻪ‬ ‫ﺑﺮاي‬ ‫ي‬
	‫ﺷﻮري‬ ‫آﺳﺘﺎﻧﻪ‬ ‫ﺣﺪ‬ ‫از‬ ‫ﺑﺎﻻﺗﺮ‬ ‫ﻫﺎي‬ ‫داده‬ ‫راﺑﻄﻪ‬ ‫از‬ ‫اﺳﺘﻔﺎده‬ ‫ﺑﺎ‬ ‫ﺷﺪن‬ ‫ﺳﺒﺰ‬ ‫درﺻﺪ‬ ‫ﻫﺎي‬ ‫ﺷﯿﺐ‬ ‫ﺑﺎ‬ ‫ﻧﺴﺒﯽ‬ ‫ﻋﻤﻠﮑﺮد‬ ) 5 (	8	‫ﺑﺮزﮔﺮ‬ ‫و‬ ‫ﯾﺎدﮔﺎري‬ .(	‫ﻧﺪاﺷﺖ‬ ) ‫راﺑﻄﻪ‬ 4 .	‫درﺻﺪ‬ ‫اﺳﺖ‬ ‫ﺷﺪه‬ ‫ﭘﯿﺸﻨﻬﺎد‬ ‫ﺷﻮري‬ ‫ﺑﻪ‬ ‫ﺟﻮاﻧﻪ‬ ‫زﻧﯽ‬ ‫ﺷﻨﺒﻠﯿﻠﻪ‬ ‫ﺑﺬر‬
	1 2 ) 2010 -‫ﺗﻮده‬ ‫ﻣﻘﺎﯾﺴﻪ‬ -‫ﺳ‬ ‫ﮐﺎﻫﺶ‬ ‫ﺷﯿﺐ‬ ‫ﺷﻮري،‬ ‫ﺑﻪ‬ ‫ﺗﺤﻤﻞ‬ ‫آﺳﺘﺎﻧﻪ‬ ‫ﺣﺪ‬ ‫ﻣﺪل‬ ‫ﺑﺮﺧﯽ‬ ‫از‬ ‫اﺳﺘﻔﺎده‬ ‫ﺑﺎ‬ ‫ﮔﯿﺎﻫﭽﻪ،‬ ‫ﺷﺪن‬ ‫ﺳﺒﺰ‬ ‫ﻣﺮﺣﻠﻪ‬ ‫در‬ ‫ﺷﻮري‬ ‫ﺑﻪ‬ ‫ﺗﺤﻤﻞ‬ ‫ﻧﻈﺮ‬ ‫از‬ ‫ﺷﻨﺒﻠﯿﻠﻪ‬ ‫ﻣﺨﺘﻠﻒ‬ ‫ﻫﺎي‬ ‫ﺑﺮاي‬ ‫ﺷﻮري‬ ‫ﺑﻪ‬ ‫ﺗﺤﻤﻞ‬ ‫ﺷﺎﺧﺺ‬ ‫ﻧﯿﺰ‬ ‫و‬ ‫ﺷﺪن‬ ‫ﺒﺰ‬ ‫ﺑﺮﺧﯽ‬ ‫ﺗﻮده‬ ‫ﺷﻨﺒﻠﯿﻠﻪ‬ ‫ﻫﺎي‬ ‫ﺷﺪ‬ ‫اﻧﺠﺎم‬ ‫ﺗﺠﺮﺑﯽ‬ ‫ﻫﺎي‬ ‫ﺷﺪ‬ ‫اراﺋﻪ‬ . ( ‫ﺑﺮ‬ ‫ﺷﻮري‬ ‫اﺛﺮ‬ ‫ﺑﺮرﺳﯽ‬ ‫در‬ ‫ﺟﻮاﻧﻪ‬ ‫زﻧﯽ‬ ‫ﭼﻨﺪﯾﻦ‬ ‫ﮔﯿﺎه‬ ‫ﮐﻪ‬ ‫دادﻧﺪ‬ ‫ﻧﺸﺎن‬ ‫داروﯾﯽ‬ ‫ﺷﻨﺒ‬ ‫ﺑﻪ‬ ‫را‬ ‫ﺗﺤﻤﻞ‬ ‫ﺑﯿﺸﺘﺮﯾﻦ‬ ‫ﻠﯿﻠﻪ‬ ‫ﺷﻮري‬ ‫داﺷﺖ‬ . ‫آزﻣﺎﯾﺸﯽ‬ ‫در‬ ‫ﺗﻨﺶ‬ ‫اﺛﺮ‬ ‫ﺷﻮري‬ ‫ﺑﺮ‬ ‫ﺟﻮاﻧﻪ‬ ‫زﻧﯽ‬ ‫ﮔﯿ‬ ‫اوﻟﯿﻪ‬ ‫رﺷﺪ‬ ‫و‬ ‫ﺷﻨﺒﻠﯿ‬ ‫ﺎﻫﭽﻪ‬ ‫ﺷﺪ‬ ‫داده‬ ‫ﻧﺸﺎن‬ ‫و‬ ‫ﺑﺮرﺳﯽ‬ ‫ﻠﻪ‬ ‫ﮐﻪ‬ ‫ﺳﺮﻋﺖ‬ ‫و‬ ‫درﺻﺪ‬ ‫ﮐﺎﻫﺶ‬ ‫ﻣﻮﺟﺐ‬ ‫ﺷﻮري‬ ‫اﻓﺰاﯾﺶ‬ ‫ﺟﻮاﻧﻪ‬ ‫زﻧﯽ‬ ، 1 Trigonella foenum-graecum L. 2 Hassanzadeh 3 Zargari 4 Petropoulos ‫ﺛﺎﺑﺘﯽ‬ ‫ﺧﻄﯽ‬ ‫ﺻﻮرت‬ ‫ﺑﻪ‬ ‫ﻣﯽ‬ ‫ﮐﺎﻫﺶ‬ ‫ﺑﻪ‬ ‫ﺷﺮوع‬ ‫ﮐﻨﺪ‬ . 1 :( ) ‫راﺑﻄﻪ‬ 1 ( Y = 100 -l (EC-a 0 ) ) ‫راﺑﻄﻪ‬ ‫ر‬ ‫اﯾﻦ‬ ‫در‬ ‫اﺑﻄﻪ،‬ Y ‫ﻧﺴﺒﯽ،‬ ‫ﻋﻤﻠﮑﺮد‬ EC ‫ﺷﻮري‬ ‫ﻣﺘﻮﺳﻂ‬ ‫ﺧﺎك،‬ ‫اﺷﺒﺎع‬ ‫ﻋﺼﺎره‬ l ‫و‬ ‫ﻋﻤﻠﮑﺮد‬ ‫ﮐﺎﻫﺶ‬ ‫ﺷﯿﺐ‬ a 0 ‫ﺣﺪ‬ ‫ﻣﯽ‬ ‫ﺷﻮري‬ ‫ﺑﻪ‬ ‫ﺗﺤﻤﻞ‬ ‫آﺳﺘﺎﻧﻪ‬ ‫ﺑﺎﺷﺪ‬ . ) ‫راﺑﻄﻪ‬ 4 ( ST-index = EC 50 + s. EC 50 ‫راﺑﻄﻪ‬ ) 5 x Arc sin ( ‫ﻧﻈﺮ‬ ‫از‬ ‫ﮔﯿﺎﻫﭽﻪ‬ ‫ﺷﺪن‬ ‫ﺳﺒﺰ‬ ‫ﻣﺮﺣﻠﻪ‬ ‫اﯾﻨﮑﻪ‬ ‫ﺑﻪ‬ ‫ﺗﻮﺟﻪ‬ ‫ﺑﺎ‬ ‫اﺳﺖ،‬ ‫اﻫﻤﯿﺖ‬ ‫ﺣﺎﺋﺰ‬ ‫ﻣﻨﺎﺳﺐ‬ ‫ﺳﺒﺰ‬ ‫درﺻﺪ‬ ‫داﺷﺘﻦ‬ ‫زاوﯾﻪ‬ ‫ﺻﻮرت‬ ‫ﺑﻪ‬ ‫ﻗﺮار‬ ‫ﺗﺠﺰﯾﻪ‬ ‫ﻣﻮرد‬ ‫ﺳﭙﺲ‬ ‫و‬ ‫ﺷﺪه‬ ‫ﺗﺒﺪﯾﻞ‬ ‫اي‬ ‫اﯾﻦ‬ ‫ﺗﺤﻘﯿﻖ‬ ‫ﻫﺪف‬ ‫ﺑﺎ‬ ‫ارزﯾﺎﺑﯽ‬ ‫ﺷﻮري‬ ‫ﺗﻨﺶ‬ ‫اﺛﺮات‬ ‫ﺑﺮ‬ ‫ﮔﺮﻓﺖ‬ . ‫داده‬ ‫ﻧﺮم‬ ‫از‬ ‫اﺳﺘﻔﺎده‬ ‫ﺑﺎ‬ ‫ﻫﺎ‬ ‫آﻣﺎري‬ ‫اﻓﺰار‬ SAS ‫ﺗﺠﺰ‬ ‫ﯾﻪ‬ ‫ﺧﺼﻮﺻﯿﺎت‬ ‫ﻣﺨﺘﻠﻒ‬ ‫ﺷﺪن‬ ‫ﺳﺒﺰ‬ ‫ﮔﯿﺎﻫﭽ‬ ‫ﻪ‬ ‫و‬ ‫ارزﯾﺎﺑﯽ‬ ‫ﻣﺪل‬ ‫ﻣﯿﺎﻧﮕﯿﻦ‬ ‫ﻣﻘﺎﯾﺴﺎت‬ ‫و‬ ‫ﺷﺪه‬ ‫داﻣﻨﻪ‬ ‫ﭼﻨﺪ‬ ‫آزﻣﻮن‬ ‫ﺑﺎ‬ ‫ﻫﺎ‬ ‫داﻧﮑﻦ‬ ‫اي‬ ‫ﻣﺨﺘﻠﻒ‬ ‫ﻫﺎي‬ ‫ﺑﺮاي‬ ‫ﺗﺠﺮﺑﯽ‬ ‫ﻣﻄﺎﻟﻌﻪ‬ ‫واﮐﻨﺶ‬ ‫ﺗﻮده‬ ‫ﺷﻨﺒﻠﯿﻠﻪ‬ ‫ﻣﺨﺘﻠﻒ‬ ‫ﻫﺎي‬ ‫ﮔﺮﻓﺖ‬ ‫اﻧﺠﺎم‬ . ‫ﻣﺪل‬ ‫ﺗﺤﻘﯿﻖ،‬ ‫اﯾﻦ‬ ‫در‬ ‫ﺗﺠﺮﺑﯽ‬ ‫ﻣﺨﺘﻠﻒ‬ ‫ﻫﺎي‬ ‫ﺑﻪ‬ ‫ﺷﻮري‬ ) ‫ﺗﻐﯿﯿﺮ‬ ‫ﻧﺰوﻟﯽ‬ ‫ﺟﺰﺋﯽ‬ ‫ﭼﻨﺪ‬ ‫و‬ ‫ﻧﻤﺎﯾﯽ‬ ‫ﺳﯿﮕﻤﻮﺋﯿﺪي،‬ ‫ﺧﻄﯽ،‬ ‫اﻧﺘﺨﺎب‬ ‫و‬ ‫ﺷﻮري‬ ‫ﺑﻪ‬ ‫ﺗﺤﻤﻞ‬ ‫آﺳﺘﺎﻧﻪ‬ ‫ﺣﺪ‬ ‫ﺗﻌﯿﯿﻦ‬ ، ‫ﻣﺘﺤﻤﻞ‬ ‫ﺗﻮده‬ ‫ﺗﺮﯾﻦ‬ ‫ﺷﺪن‬ ‫ﺳﺒﺰ‬ ‫ﻣﺮﺣﻠﻪ‬ ‫در‬ ‫ﻫﺎ‬ ‫ﮔﺮﻓﺖ‬ ‫اﻧﺠﺎم‬ ‫ﯾﺎﻓﺘﻪ‬ ( ‫ﺗﻮده‬ ‫واﮐﻨﺶ‬ ‫ارزﯾﺎﺑﯽ‬ ‫ﺑﺮاي‬ ‫ﺷﻮري‬ ‫ﺑﻪ‬ ‫ﺷﻨﺒﻠﯿﻠﻪ‬ ‫ﻫﺎي‬ . ‫و‬ ‫ﮔﺮﻓﺖ‬ ‫ﻗﺮار‬ ‫ﺑﺮرﺳﯽ‬ ‫ﻣﻮرد‬ ‫ﺗﺤﻤﻞ‬ ‫آﺳﺘﺎﻧﻪ‬ ‫ﺣﺪ‬ ‫اراﺋﻪ‬ ‫ﺿﻤﻦ‬
	‫واﺣﺪ‬ ‫ﻫﺮ‬ ‫ازاي‬ ‫ﺑﻪ‬ ‫ﺷﺪن‬ ‫ﺳﺒﺰ‬ ‫ﮐﺎﻫﺶ‬ ‫ﺷﯿﺐ‬	‫ﺷﻮري،‬ ‫ﺑﻪ‬	5 Mehrafarin
	‫ﻣﺤﺎﺳﺒﻪ‬	‫ﺑﺎ‬	‫ﻫﻤﭽﻨﯿﻦ،‬	‫ﮔﺮدﯾﺪ‬ ‫ﺑﺮآورد‬ ‫ﺷﻮري‬ ‫اﻓﺰاﯾﺶ‬ .	6 Tsay 7 Dadkhah 1 Van Genuchten and Hoffman 2 Steppuhn
												8 Yadegari and Barzegar 3 ST-index

s ‫ﻋﻤﻠﮑﺮد‬ ‫ﺗﻐﯿﯿﺮات‬ ‫از‬ ‫ﮐﻪ‬ ‫اﺳﺖ‬ ‫ﻣﻌﺎدﻟﻪ‬ ‫ﺷﯿﺐ‬ ، ‫و‬ ‫ﺷﺪه‬ ‫ﺣﺎﺻﻞ‬ ‫ﻣﺤﯿﻂ‬ ‫ﺷﻮري‬ ‫ﺗﻐﯿﯿﺮات‬ ‫ﺑﻪ‬ ‫ﻧﺴﺒﺖ‬ ‫ﻧﺴﺒﯽ‬ ‫ﻧﻤﺎﯾﯽ‬ ‫ﻋﺒﺎرت‬ 
Table 1 .

 1 Chemical analysis of highly saline water (diluted with tap water of 1:20 ratio) 


	‫ﻫﺪاﯾﺖ‬ ‫اﻟﮑﺘﺮﯾﮑﯽ‬ EC (dS/cm)	pH	CO 3	2-	Anions .) meq/lit ‫آﻧ‬ ‫ﯿ‬ ‫ﻮن‬ ( Cl -HCO 3 -	SO 4	2-	Ca 2+	Cations .) meq/lit ‫ﮐﺎﺗ‬ ‫ﯿ‬ ‫ﻮن‬ ( Na + Mg 2+	K +	‫ﻧﺴﺒﺖ‬ ‫ﺟﺬب‬ ‫ﺳﺪﯾ‬ ‫ﻢ‬ SAR	‫ﺷﺎﺧﺺ‬ ‫ﮔﺮﻓﺘﮕﯽ‬ RSC
	25	7.94	0		2.77	223.11	19.5	4.05	29.52	211.3	0.51	51.57	-30.8
						‫ﺷﻨﺒﻠﯿﻠﻪ‬	‫ﺷﺪه‬ ‫ﮔﯿﺮي‬	‫اﻧﺪاز‬ ‫ﻣﺨﺘﻠﻒ‬ ‫ﺻﻔﺎت‬ ‫ﻣﺮﺑﻌﺎت‬ ‫ﻣﯿﺎﻧﮕﯿﻦ‬ ‫ﺑﺮاي‬ ‫وارﯾﺎﻧﺲ‬ ‫ﺗﺠﺰﯾﻪ‬ ‫ه‬	.	2	‫ﺟﺪول‬

Table 2 .

 2 Analysis of variance for mean squar of different measured traits of fenugreek 


	‫ﺗﻐﯿﯿﺮ‬ ‫ﻣﻨﺎﺑﻊ‬ Sources of variance	‫درﺟﻪ‬ ‫آزادي‬ df	‫ﺷﺪن‬ ‫ﺳﺒﺰ‬ ‫درﺻﺪ‬ Emergence percentage	‫ﺳﺒﺰ‬ ‫ﺳﺮﻋﺖ‬ ‫ﺷﺪ‬ ‫ن‬ rate Emergence	‫رﯾﺸﻪ‬ ‫ﻃﻮل‬ Root length	‫ﻃﻮل‬ Stem ‫ﺳﺎﻗﻪ‬ length	‫ﺑﻨﯿﻪ‬ ‫ﺷﺎﺧﺺ‬ ‫ﮔﯿﺎﻫﭽﻪ‬ vigour index Seedling	‫ﮔﯿﺎﻫﭽ‬ ‫وزن‬ ‫ﻪ‬ Seedling weight	‫ﮔﯿﺎﻫﭽﻪ‬ ‫ﻃﻮل‬ Seedling length
	‫ﺷﻮري‬		6	1795.5**	55.03**	252.99**	42.44**	725.31**	1819.60** 500.26**
	Salinity							
		‫ﺗﻮده‬		4	123.37**	2.13**	4.24**	5.60**	21.78**	287.33**	19.45**
	Ecotype							
	‫ﺷﻮري‬ × ‫ﺗﻮده‬	24	15.75**	0.449**	1.128**	0.634**	3.533**	71.369**	1.945**
	Salinity×ecotype						
		‫ﺧﻄﺎ‬		70	5.134	0.066	0.227	0.093	0.518	0.992	0.380
	Error							
	(	) %	‫ﺗﻐﯿﯿﺮات‬ ‫ﺿﺮﯾﺐ‬		11.487	8.794	5.474	7.177	7.912	4.923	4.762
	Coeficient of variation (%)					
			**	: significant at the level of 1%				1 %	‫ﻣﻌﻨﯽ‬ ‫ﺳﻄﺢ‬ ‫در‬ ‫دار‬	:	**

Table 3 .

 3 Fitted equations for responses of fenugreek to salinity at seedling emergence stage using experimental models 


	‫ﺗﻮده‬		‫ﻣﺪل‬					‫ﻣﺮﺟﻊ‬	‫راﺑﻄﻪ‬		‫ﺷﺪه‬ ‫داده‬ ‫ﺑﺮازش‬	‫راﺑﻄﻪ‬
	Ecotype	Model		Reference equation		Fitted equation
			‫ﺧﻄﯽ‬ ‫ﻗﺴﻤﺘﯽ‬ ‫ﺳﻪ‬ Three-piece linear I	Y=100-l*(EC-a 0 )	Y=100-6.95*(EC-4.69), r 2 =0.943
	‫اردﺳﺘﺎﻧﯽ‬	‫ﺳﯿﮕﻤﻮﺋﯿﺪي‬ Sigmoidal II	Y=Y m /1+(EC/EC 50 ) p	Y=Y m /1+(EC/11.58) 4.27 , r 2 =0.983
	Ardestani	‫ﯾﺎﻓﺘﻪ‬ ‫ﺗﻐﯿﯿﺮ‬ ‫ﻧﺰوﻟﯽ‬ ‫ﺟﺰﺋﯽ‬ ‫ﭼﻨﺪ‬ Modified multi-component III	50 Y=Y m /1+(EC/EC 50 ) exp(s× EC )	Y=Y m /1+(EC/11.58) exp1.452 , r 2 =0.983
			‫دوﮔﺎﻧﻪ‬ ‫ﻧﻤﺎﯾﯽ‬ ‫ﻋﺎﻣﻞ‬ Duble expontial factor IV	Y=100*exp[a(EC)-b(EC) 2 ]	Y=100*exp[0.0271(EC)-0.00757(EC) 2 ], r 2 =0.978
			‫ﺧﻄﯽ‬ ‫ﻗﺴﻤﺘﯽ‬ ‫ﺳﻪ‬ Three-piece linear I	Y=100-l*(EC-a 0 )	Y=100-7.25*(EC-4.90), r 2 =0.917
	‫ﻔﻬﺎﻧﯽ‬	‫اﺻ‬	‫ﺳﯿﮕﻤﻮﺋﯿﺪي‬ Sigmoidal II	Y=Y m /1+(EC/EC 50 ) p	Y=Y m /1+(EC/11.47) 4.78 , r 2 =0.972
	Isfahani	‫ﯾﺎﻓﺘﻪ‬ ‫ﺗﻐﯿﯿﺮ‬ ‫ﻧﺰوﻟﯽ‬ ‫ﺟﺰﺋﯽ‬ ‫ﭼﻨﺪ‬ Modified multi-component III	50 Y=Y m /1+(EC/EC 50 ) exp(s× EC )	Y=Y m /1+(EC/11.47) exp1.564 , r 2 =0.972
			‫دوﮔﺎﻧﻪ‬ ‫ﻧﻤﺎﯾﯽ‬ ‫ﻋﺎﻣﻞ‬ Duble expontial factor IV	Y=100*exp[a(EC)-b(EC) 2 ]	Y=100*exp[0.0304(EC)-0.00803(EC) 2 ], r 2 =0.955
			‫ﺧﻄﯽ‬ ‫ﻗﺴﻤﺘﯽ‬ ‫ﺳﻪ‬ Three-piece linear I	Y=100-l*(EC-a 0 )	Y=100-7.55*(EC-7.83), r 2 =0.804
	‫ﻫﻨﺪي‬	‫ﺳﯿﮕﻤﻮﺋﯿﺪي‬ Sigmoidal II	Y=Y m /1+(EC/EC 50 ) p	Y=Y m /1+(EC/14.24) 5.29 , r 2 =0.936
	Hendi	‫ﯾﺎﻓﺘﻪ‬ ‫ﺗﻐﯿﯿﺮ‬ ‫ﻧﺰوﻟﯽ‬ ‫ﺟﺰﺋﯽ‬ ‫ﭼﻨﺪ‬ Modified multi-component III	50 Y=Y m /1+(EC/EC 50 ) exp(s× EC )	Y=Y m /1+(EC/14.24) exp1.665 , r 2 =0.936
			‫دوﮔﺎﻧﻪ‬ ‫ﻧﻤﺎﯾﯽ‬ ‫ﻋﺎﻣﻞ‬ Duble expontial factor IV	Y=100*exp[a(EC)-b(EC) 2 ]	Y=100*exp[0.0240(EC)-0.00505(EC) 2 ], r 2 =0.887
			‫ﺧﻄﯽ‬ ‫ﻗﺴﻤﺘﯽ‬ ‫ﺳﻪ‬ Three-piece linear I	Y=100-l*(EC-a 0 )	Y=100-5.13*(EC-1.69), r 2 =0.954
	‫ﻣﺸﻬﺪي‬	‫ﺳﯿﮕﻤﻮﺋﯿﺪي‬ Sigmoidal II	Y=Y m /1+(EC/EC 50 ) p	Y=Y m /1+(EC/11.07) 2.57 , r 2 =0.926
	Mashhadi	‫ﯾﺎﻓﺘﻪ‬ ‫ﺗﻐﯿﯿﺮ‬ ‫ﻧﺰوﻟﯽ‬ ‫ﺟﺰﺋﯽ‬ ‫ﭼﻨﺪ‬ Modified multi-component III	50 Y=Y m /1+(EC/EC 50 ) exp(s× EC )	Y=Y m /1+(EC/11.07) exp0.945 , r 2 =0.926
			‫دوﮔﺎﻧﻪ‬ ‫ﻧﻤﺎﯾﯽ‬ ‫ﻋﺎﻣﻞ‬ Duble expontial factor IV	Y=100*exp[a(EC)-b(EC) 2 ]	Y=100*exp[-0.009(EC)-0.00455(EC) 2 ], r 2 =0.948
			‫ﺧﻄﯽ‬ ‫ﻗﺴﻤﺘﯽ‬ ‫ﺳﻪ‬ Three-piece linear I	Y=100-l*(EC-a 0 )	Y=100-4.63*(EC-1.57), r 2 =0.936
	‫ﻧﯽ‬ ‫رﯾﺰي‬	‫ﺳﯿﮕﻤﻮﺋﯿﺪي‬ Sigmoidal II	Y=Y m /1+(EC/EC 50 ) p	Y=Y m /1+(EC/11.71) 2.16 , r 2 =0.931
	Neyrizi	‫ﯾﺎﻓﺘﻪ‬ ‫ﺗﻐﯿﯿﺮ‬ ‫ﻧﺰوﻟﯽ‬ ‫ﺟﺰﺋﯽ‬ ‫ﭼﻨﺪ‬ Modified multi-component III	50 Y=Y m /1+(EC/EC 50 ) exp(s× EC )	Y=Y m /1+(EC/11.71) exp0.770 , r 2 =0.931
			‫دوﮔﺎﻧﻪ‬ ‫ﻧﻤﺎﯾﯽ‬ ‫ﻋﺎﻣﻞ‬ Duble expontial factor IV	Y=100*exp[a(EC)-b(EC) 2 ]	Y=100*exp[-0.017 (EC)-0.00329(EC) 2 ], r 2 =0.936
	(I: Mass, 1990; II: Van Genuchten and Hoffman, 1984; III: Steppuhn et al., 2005; IV: Wang et al., 2002)
	‫ﺣﺪاﮐﺜﺮ‬	‫ﺷﺪن،‬ ‫ﺳﺒﺰ‬ ‫ﮐﺎﻫﺶ‬ ‫ﺷﯿﺐ‬ :EC 50	‫ﺷﻮري،‬ ‫ﺑﻪ‬ ‫ﺗﺤﻤﻞ‬ ‫آﺳﺘﺎﻧﻪ‬ ‫ﺣﺪ‬ :l	a 0	‫ﺷﻮر،‬ ‫ﻏﯿﺮ‬ ‫ﺷﺮاﯾﻂ‬ ‫در‬ ‫ﻋﻤﻠﮑﺮد‬ ‫ﺣﺪاﮐﺜﺮ‬	:	Y m	‫ﻧﺴﺒﯽ،‬	‫ﻋﻤﻠﮑﺮد‬	:Y	‫ﻣﻌﺎدﻻت،‬ ‫اﯾﻦ‬ ‫در‬
			.	‫ﺑﺎﺷﻨﺪ‬	‫ﻣﯽ‬ ‫ﻣﻌﺎدﻟﻪ‬ ‫ﻫﺮ‬ ‫ﺛﺎﺑﺖ‬ ‫ﺿﺮاﯾﺐ‬	:	b	‫و‬	a	‫ﻣﻨﺤﻨﯽ‬ ‫ﺷﯿﺐ‬ ،	‫ﺗﺠﺮﺑﯽ،‬ ‫ﺛﺎﺑﺖ‬ :s	:p	‫ﻣﯽ‬ ‫ﮐﺎﻫﺶ‬ ‫ﯾﺎﺑﺪ،‬	50	%	‫ﻋﻤﻠﮑﺮد‬ ‫آن‬ ‫در‬ ‫ﮐﻪ‬ ‫ﺷﻮري‬

Table 4 .

 4 Response of some fenugreek ecotypes to salinity acording to linear and sigmoidal models at seedling emergance stage Sigmoidal equation coefficients and salt tolerance index of some fenugreek ecotypes 


	...	‫ﯿ‬ ‫ﻠﻪ‬	‫ﺷﻨﺒﻠ‬	‫ﻫﺎ‬ ‫ي‬	‫ﺗﻮده‬	‫ﯽ‬	‫ﺑﺮﺧ‬	‫ي‬	‫ﺷﻮر‬	‫ﺑﻪ‬ ‫ﺗﺤﻤﻞ‬ ‫آﺳﺘﺎﻧﻪ‬ ‫ﺣﺪ‬	‫ﯿﯿ‬ ‫ﻦ‬	‫ﺗﻌ‬ ‫و‬	‫ﯽ‬	‫ﺎﺑ‬	‫ﯾ‬	‫ارز‬	:
	‫ﭘﯿﺶ‬ ‫ﻣﺪل‬ ‫وﺳﯿﻠﻪ‬ ‫ﺑﻪ‬ ‫ﺷﺪه‬ ‫ﺑﯿﻨﯽ‬	EC 50	‫ﻣﻘﺎدﯾﺮ‬ ‫ﻣﻘﺎﯾﺴﻪ‬	‫و‬ ‫اﺳﺘﻔﺎن‬	)	‫ﯾﺎﻓﺘﻪ‬ ‫ﺗﻐﯿﯿﺮ‬ ‫ﺳﯿﮕﻤﻮﺋﯿﺪي‬ ‫ﻣﺪل‬ ‫اﺳﺎس‬ ‫ﺑﺮ‬
	‫ﮐﻪ‬ ‫داد‬ ‫ﻧﺸﺎن‬ ‫ﻗﺴﻤﺘﯽ،‬ ‫ﺳﻪ‬ ‫ﺧﻄﯽ‬ ‫ﻣﺪل‬ ‫ﺑﺎ‬ ‫ﺳﯿﮕﻤﻮﺋﯿﺪي‬	b 2005 ( ‫ﻣﻘﺪار‬ ،	2005 ‫ﻫﻤﮑﺎران،‬ ‫و‬ ‫اﺳﺘﻔﺎن‬ ‫؛‬	a	‫ﻤﮑﺎران،‬	‫ﻫ‬
	‫ﺷ‬ ‫ﻣﻘﺪار‬ ‫ﮔﯿﺎﻫﭽﻪ‬ ‫ﺷﺪن‬ ‫ﺳﺒﺰ‬ ‫درﺻﺪ‬ ‫آن‬ ‫در‬ ‫ﮐﻪ‬ ‫ﻮري‬ ‫ﺑﻪ‬ ‫ﻫﺎ‬	‫ﭘﯿﺶ‬ ‫ﺑﯿﻨﯽ‬	EC 50	‫ﺗﻮده‬ ‫ﻣﻘﺎدﯾﺮ‬ ‫ﺑﺮاﺑﺮ‬ ‫ﺷﻨﺒﻠﯿﻠﻪ‬ ‫ﻫﺎي‬	EC 50
	‫ﺷﻨﺒﻠﯿﻠﻪ‬ ‫ﻫﺎي‬	‫ﺗﻮده‬ ‫ﺗﻤﺎم‬ ‫ﺑﺮاي‬ ‫ﯾﺎﺑﺪ‬	‫ﻣﯽ‬ ‫ﮐﺎﻫﺶ‬	% 50	‫ﻣﯿﺰان‬	) ‫و‬ ‫واﻧﮕﻨﻮﺧﺘﻦ‬	‫ﻣﻌﻤﻮﻟﯽ‬ ‫ﺳﯿﮕﻤﻮﺋﯿﺪي‬ ‫ﻣﺪل‬ ‫وﺳﯿﻠﻪ‬ ‫ﺑﻪ‬ ‫ﺷﺪه‬
	‫ﺳﯿﮕ‬ ‫ﻣﺪل‬ ‫ﻣﺸﺎﺑﻪ‬ ‫ﺑﺮرﺳﯽ‬ ‫ﻣﻮرد‬ ‫ﻤ‬ ‫اﺧﺘﻼف‬ ‫و‬ ‫ﺑﻮده‬ ‫ﻮﺋﯿﺪي‬	.	‫ﺑﻮد‬	1984 (	‫ﻫﺎﻓﻤﻦ،‬
					.(	1	‫ﺷﮑﻞ‬	)	‫داد‬ ‫ﻧﺸﺎن‬ ‫آن‬ ‫ﺑﺎ‬ ‫اﻧﺪﮐﯽ‬
						‫اردﺳﺘﺎﻧﯽ‬						‫اﺻﻔﻬﺎﻧﯽ‬
					Ardestani					Isfahani
								‫ﻫﻨﺪي‬									‫ﻣﺸﻬﺪي‬
						Hendi							Mashhadi

‫ﮔﯿﺎﻫﭽﻪ‬ ‫ﺷﺪن‬ ‫ﺳﺒﺰ‬ ‫ﻣﺮﺣﻠﻪ‬ ‫در‬ ‫ﺳﯿﮕﻤﻮﺋﯿﺪي‬ ‫و‬ ‫ﺧﻄﯽ‬ ‫ﻣﺪل‬ ‫اﺳﺎس‬ ‫ﺑﺮ‬ ‫ﺷﻮري‬ ‫ﺑﻪ‬ ‫ﺷﻨﺒﻠﯿﻠﻪ‬ ‫ﻫﺎي‬ Fig. 1. 
Table 5 .

 5 Interaction of the effect of salinity and ecotype on the studied traits of fenugreek at seedling emergence satage based on the duncan test p<0.05. In each column, means with at least a same letter are not significantly different from each other at p˂0.05. ‫ﺷﻨﺒﻠﯿﻠﻪ،‬ ‫در‬ ‫ﮐﻪ‬ ‫داد‬ ‫ﻧﺸﺎن‬ ‫ﻣﺨﺘﻠﻒ‬ ‫ﻣﻨﺎﺑﻊ‬ ‫ﺑﺮرﺳﯽ‬ ‫ﺗﻮﺟﻪ‬ ‫ﻣﻮرد‬ ‫ﮐﻤﺘﺮ‬ ‫ﺷﺪن‬ ‫ﺳﺒﺰ‬ ‫ﻣﺮﺣﻠﻪ‬ ‫در‬ ‫ﺷﻮري‬ ‫ﺑﻪ‬ ‫واﮐﻨﺶ‬ ‫اﻏﻠﺐ‬ ‫ﺷﻮري‬ ‫زﻣﯿﻨﻪ‬ ‫در‬ ‫ﺷﺪه‬ ‫اﻧﺠﺎم‬ ‫ﺗﺤﻘﯿﻘﺎت‬ ‫و‬ ‫ﮔﺮﻓﺘﻪ‬ ‫ﻗﺮار‬ 


	‫ﺷﻮري‬ Salinity (dS/m)	‫ﺗﻮده‬ Ecotype	‫ﺷﺪن‬ ‫ﺳﺒﺰ‬ ‫درﺻﺪ‬ Emergence percentage		‫ﺷﺪن‬ ‫ﺳﺒﺰ‬ ‫ﺳﺮﻋﺖ‬ Emergence rate (n/day)	‫رﯾﺸﻪ‬ ‫ﻃﻮل‬ Root length (cm)	‫ﺳﺎﻗﻪ‬ ‫ﻃﻮل‬ Stem length (cm)	‫ﺑﻨﯿﻪ‬ ‫ﺷﺎﺧﺺ‬ ‫ﮔﯿﺎﻫﭽﻪ‬ Seedling vigour	‫ﮔﯿﺎﻫﭽﻪ‬ ‫وزن‬ Seedling weight (mg)	‫ﮔﯿﺎﻫﭽﻪ‬ ‫ﻃﻮل‬ Seedling length (cm)
																	index
	Ardestani		89.25cd			4.66c		13.92abc	4.54jk	16.47cd	25.27h	18.46ef
		Isfahani		88.17cd			5.58ab	13.86bc	7.24ab	18.62b	44.80b	21.11b
	0.5		Hendi		94.62a				5.79ab	14.07abc	6.51cd	19.48ab	31.33ef	20.58bc
	Mashhadi		91.40bc			5.93a		14.68a	7.71a	20.44a	49.40a	22.39a
		Neyrizi		92.47ab			5.68ab	14.53ab	6.79bc	19.73ab	31.67ef	21.33b
	Ardestani		84.95def			4.09de	12.33d	4.79ij	14.54ef	20.45i	17.11gh
		Isfahani		83.87def			4.71c		12.77d	5.91efg	15.68de	37.42c	18.69ef
	3		Hendi		88.17cde			4.81c		13.63c	6.14de	17.43c	30.07f	19.77cd
	Mashhadi		81.72efg			4.42cd	13.84bc	5.54fgh	15.83d	24.87h	19.37de
		Neyrizi		87.09cde			5.47b		12.75d	5.95ef	16.28cd	30.85ef	18.70ef
	Ardestani		78.42fghi			3.44ghi	9.30g	3.94lmn	10.38gh	16.34jkl	13.24jk
		Isfahani		78.49fgh			4.02def	12.5d	5.42gh	14.14f	33.40d	18.00fg
	6		Hendi		86.02cde			4.12de	11.21e	5.78efg	14.61ef	27.69g	16.99h
	Mashhadi		69.89ij				3.32hi	10.28f	5.45gh	11.01gh	32.42de	15.73i
		Neyrizi		73.12hij			4.13de	10.43ef	5.21hi	11.44g	27.38g	15.65i
	Ardestani		66.67jk			2.58kl	8.11h	3.82mno	7.96i	17.77j	11.93l
		Isfahani		72.04hij			3.80efg	9.13g	5.05hi	10.23h	17.20jk	14.19j
	9		Hendi		82.80defg			3.63fgh	8.14h	5.15hi	10.99gh	19.70i	13.29jk
	Mashhadi		59.14kl			2.86jk	8.03h	4.33jkl	7.34i	12.51mn	12.36kl
		Neyrizi		55.91lm			2.75jk	8.20h	4.26klm	6.97i	24.74h	12.46kl
	Ardestani		45.16mn			1.87n		5.09jk	2.60st	3.47kl	7.71p	7.69op
		Isfahani		36.56no			1.14op	5.77j	3.10pqr	3.24kl	16.03kl	8.87n
	12		Hendi		75.27ghij			3.08ij		6.64i	3.58nop	7.68i	13.37m	10.23m
	Mashhadi		50.54lm			1.90mn	5.54j	2.73rst	4.18k	12.01mn	8.27no
		Neyrizi		51.61lm			2.29lm	7.10i	3.44opq	5.45j	19.43i	10.54m
	Ardestani		20.43qr			0.56rst	3.63mn	2.53t	1.27no	7.04pq	6.17qr
		Isfahani		22.58pq			0.70qr	5.27jk	3.03qrs	1.88mn	11.27no	8.30no
	15		Hendi		32.26opq			0.99opq	5.60j	2.73rst	2.69lm	10.37o	8.33no
	Mashhadi		29.03opq			0.98opq	4.53kl	2.48t	2.03mn	11.50no	7.02pq
		Neyrizi		33.33op			1.16o		5.19jk	3.13pqr	2.77lm	15.10l	8.32no
	Ardestani		8.60rs				0.27st	3.33n	1.27v	0.39o	4.45s	4.60s
		Isfahani		6.45s				0.16t			4.23lm	2.73rst	0.45o	6.50pqr	6.97pq
	18		Hendi		25.81opq			0.73pqr	3.53mn	1.97u	1.42no	5.60qrs	5.50rs
	Mashhadi		9.68rs				0.25t			3.45n	1.95u	0.53o	7.20pq	5.40rs
		Neyrizi		22.58pq			0.67qrs	3.78lmn	1.88u	1.28no	5.13rs	5.67r
		‫ﻧﯿﺴﺘﻨﺪ‬ .	‫درﺻﺪ‬	5	‫ﺳﻄﺢ‬ ‫در‬	‫دار‬ ‫ﯾﮑﺪﯾﮕﺮ‬ ‫ﺑﺎ‬ ‫ي‬	‫ﻣﻌﻨﯽ‬	‫اﺧﺘﻼف‬	‫داراي‬	‫ﺑﺎﺷﻨﺪ‬ ،	‫ﯾﮑﺴﺎن‬	‫ﺣﺮف‬ ‫ﯾﮏ‬	‫داراي‬	‫ﺣﺪاﻗﻞ‬	‫ﻣﯿﺎﻧﮕﯿﻦ‬ ‫ﮐﻪ‬ ‫ﻫﺎﯾﯽ‬	‫ﺳﺘﻮن،‬	‫ﻫﺮ‬ ‫در‬
	‫و‬ ‫ﻋﺒﺪاﻟﻤﻮﻣﻦ‬	2010 ‫؛‬	‫دادﺧﻮاه،‬	)	‫اﻧﺪ‬	‫داده‬ ‫ﻗﺮار‬ ‫ﻣﻄﺎﻟﻌﻪ‬
	.	2011 (	‫ﺣﺴﯿﻦ،‬ ‫و‬ ‫زﻫﯿﺮ‬	2009 ‫؛‬	‫اﻻدرﯾﺴﯽ،‬ ‫ﻣﺼﺒﺎح‬
	‫زﻣﺎن‬ ‫در‬	‫ﮔﯿﺎﻫﺎن‬ ‫ﺑﺮﺧﯽ‬ ‫ﮐﻪ‬ ‫اﺳﺖ‬ ‫ﺷﺪه‬ ‫ﮔﺰارش‬
	‫ﺑﻮﺗـﻪ‬ ‫اﺳـﺘﻘﺮار‬ ‫و‬ ‫ﺷـﺪن‬ ‫ﺳﺒﺰ‬ ،	‫زﻣـﺎن‬ ‫ﺑﻪ‬ ‫ﻧﺴﺒﺖ‬	‫ﯽ‬	‫ﺟﻮاﻧﻪ‬ ‫زﻧ‬	‫ر‬ ‫اﺣﻞ‬ ‫ﺷﺪ‬	‫ﻣﺮ‬ ‫ﮐﻤﯽ‬ ‫ﺗﻌﺪاد‬ ‫و‬	‫ﺑﻮده‬ ‫زﻧﯽ‬	‫ﺟﻮاﻧﻪ‬ ‫ﻣﺮﺣﻠﻪ‬ ‫در‬
																	‫ﻣﻮرد‬ ‫را‬ ‫داﻧﻪ‬ ‫ﻋﻤﻠﮑﺮد‬ ‫و‬ ‫زاﯾﺸﯽ‬ ‫رﺷﺪ‬ ‫ﻧﺪرت‬ ‫ﺑﻪ‬ ‫و‬	‫روﯾﺸﯽ‬

، 2017 .( 1 Hagemeyer 2 Ranjbar and Ghadiri
‫ز‬ ‫رﮔﺮي‬, Roumani And Ehteshami, Vimala 12 Chowdhury, Missbah El, Hoffman Maas, Mohammad Hossein Banakar, Hamzeh Amiri, Gholam Hassan Ranjbar, Mohammad Reza Sarafraz
‫آﺳﺘﺎ‬ ‫ﺣﺪ‬ ‫ﺗﻌﯿﯿﻦ‬ ‫و‬ ‫ارزﯾﺎﺑﯽ‬ ‫ﺷﻮري‬ ‫ﺑﻪ‬ ‫ﺗﺤﻤﻞ‬ ‫ﻧﻪ‬ ‫ﺗﻮده‬ ‫ﺑﺮﺧﯽ‬ ‫ﺷﻨﺒﻠﯿﻠﻪ‬ ‫ﻫﺎي‬ ) Trigonella foenumgraecum ( ‫ﺷﺪن‬ ‫ﺳﺒﺰ‬ ‫ﻣﺮﺣﻠﻪ‬ ‫در‬ ‫ﮔﯿﺎﻫﭽﻪ‬