ہک دھی رانی دی فریاد
بولے جدوں بنیرے کاں
میں سمجھ جاندی ہاں
گل ہے ضرور اولی
تاہیوں کردا اے کاں کاں
کائی دس پیغام خوشی دا
مینوں درداں ماریا تھاں
میں کٹھی وچ ہجر دے
میری نکلی جاندی جاں
میرے سینے پھٹ انوکھا
کر سکدی نہیں عیاں
میری سن فریاد اے امبڑی
جے توں ہیں میری ماں
نہیں سُجھدے ریشم گوٹے
نہ محل چوبارے تھاں
نہ چوڑے ہار حمیلاں
نہ کنٹھا منگدی ہاں
نہ گانی نتھ نہ ِٹکّا
نہ منگاں حویلی تھاں
نہ ریشم لہنگے منگاں
نہ سونا چاندی چاہاں
نہ ہور قصیدے چوڑے
نہ قریشیے بانہاں
نہ مربعے، بھوئیں نہ بھانڈے
نہ کوئی لمبی……… لاں
نہ ریجھ مایا دی مینوں
نہ مجھ نہ وچھا گاں
ہک راز دلے وچ میرے
دس میں ہن کی کراں
تیرے لکھ احسان کروڑاں
بھل سکاں میں کداں
تیرا حکم میرے سر اکھیں
توں سکی میری ماں
اک خیر منگاں میں تیتھوں
نالے منگدی وی سنگاں
کر سکدی توں ہیں اماں
میری زندگی میرے ناں
جے میری گل توں منیں
میں اُڈّاں باہجھ پراں
جے نال رنجیٹھے ٹوریں
دل ٹھردا میرا تاں
The use of similes, metaphors, proverbs and idioms is given its due prestige in the annals of literature. To mention their use in the Islamic literature especially in the sayings of our Holy Prophet (PBUH) renders an ease and comfort in order to elaborate upon the Islamic teachings. It not only enhances interest but renders an inexplicable charm to explicate Islamic teachings so as to make them easy to comprehend. The use of figurative language enhances the rhythmic flow and charm of language and thus brings in a huge impact on literature. It is in this way that the proselytization task be done in an easy effective manners.
Industrial colored wastewater plays an important role in environment pollution. In present study, the removal of synthetic acid dyes was carried out in batch and column mode with biocomposites using biosorption technology. The effect of different experimental parameters such as pH, biosorbent dose, initial dye concentration, contact time and temperature were determined to investigate the optimum conditions for attaining the maximum removal of acid dyes. The optimum pH for getting the maximum biosorption of four selected acid dyes (ADG-180, AO-RL, ANB N-RBL and ATB E-2G) was observed in acidic range (2-6) while the 0.05 g/50 mL biosorbent dose (PPy/SB, PAn/SB, PPy/Ch, PAn/Ch, PPy/St and PAn/St; PPy/RH, PAn/RH, PPy/Ch, PAn/Ch, PPy/St and PAn/St; PPy/PH, PAn/PH, PPy/Ch, PAn/Ch, PPy/St and PAn/St and PPy/CS, PAn/CS, PPy/Ch, PAn/Ch, PPy/St and PAn/St ) was determined as optimum dose for the removal of all four selected acid dyes respectively. The equilibrium was attained within 45-60 min for all selected biosorbents for the elimination of selected acid dyes. The initial dye concentration in the range of 125-150 mg/L was considered as optimum for getting the maximum elimination of acid dyes using different types of selected biosorbents. The optimum temperature for getting maximum removal of all selected acid dyes was observed as 30 ºC and reduction in biosorption capacity of all biosorbents was investigated with the rise of temperature. It showed the exothermic nature of all biosorption processes involved in the removal of selected acid dyes. Both Langmuir and Freundlich biosorption isotherms showed the satisfactorily fitness on equilibrium biosorption data where as the pseudo-first-order and pseudo-second-order both showed the satisfactory fitness on biosorption kinetic data. Different thermodynamic parameters were determined to understand the nature and feasibility of biosorption process. The significant effect of different concentrations of electrolytes and heavy metal ions on the biosorption potential of selected most efficient biosorbent for the removal of their respective acid dyes was observed. The biosorption efficiency of selected efficient biosorbent for respective acid dyes was reduced significantly in the presence of surfactants/detergents in dye solution. Maximum desorption was achieved using 0.5 N NaOH. In column study, optimum bed height, flow rate and inlet dye concentration were found to be 3 cm, 1.8 mL/min and 70 mg/L for the achievement of maximum biosorption of ADG-180, AO-RL, ANB N-RBL and 90 mg/L for ATB E-2G dye. The biosorption study of real textile effluents was also carried out for the application of this technology on practical scale. The characterization of biosorbents was carried out using thermal analysis, FT-IR and SEM which provided the information about thermal stability, active binding functional groups and surface morphology.