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IOSR Journal of Environmental Science, Toxicology and Food Technology (IOSR-JESTFT)
e-ISSN: 2319-2402,p- ISSN: 2319-2399.Volume 9, Issue 11 Ver. II (Nov. 2015), PP 114-116
www.iosrjournals.org
DOI: 10.9790/2402-09112114116 www.iosrjournals.org 114 | Page
Effect Of Mat(Cyprus Rotundis) Industry Effluents On
Biomolecules In Leaves Of Lablab Purpureus(L.)
Dr. C.Sumathy
Assistant Professor In Biochemistry Department
MIET Arts And Science College, Trichirapalli, Tamilnadu, India.
Abstract: The effect of mat (Cyprus rotundis) industry effluent in different concentrations (viz. 5%, 10%, 15%,
25%, 30%, 35%, 40%, 45%, 50% ) on the biochemical constituents in leaves of Lablab purpureus(L.) was
studied . Ground water treated plants were used as control and as well as diluent. Physico-chemical, Elemental
analysis of effluent and ground water were also studied .Biochemical constituents like total soluble sugars, free
aminoacids, total soluble starch, total soluble proteins,free proline, total lipids were decreased with increasing
effluent concentration.
Key words:- biochemical, constituents, diluent, effluent,physico-chemical.
I. Introduction
Water is a vital source for all kinds of life on planet; on the other hand, it is also a resource that is
adversly affected both quantitatively and qualitatively due to urbanization , industrialization and other human
activities. Even the ground water, which is supposed to be pure, is affected due to contamination of effluent
discharged from industries containing decomposing matter and industrial wastes. So it becomes necessary to
find out the level of pollution in water sources and examine if they are hazardous to plant.The mat industry is
more than 250 years old. The woven mats are then polished with smooth river stones and their edges bound.
While the superfine quality mats are fit enough to grace palaces and become part of a bridal troussea, the coarser
ones are used all over Tamilnadu for sitting and sleeping, fancy wall fitting in cottages and hotels. Dyes contain
metals such as copper, nickel, chromium, mercury and cobalt. In some dyes, these metals are integral to the
dye's molecule; in others, they present as impurities. Metals are difficult to remove from waste water and may
escape the capacities of the effluent treatment system. If the system manages to remove them, they become part
of the sludge rendering it toxic.
The coloured dye effluents are considered to be highly toxic to the aquatic biota and affect the
symbiotic process by disturbing the natural equilibrium through reducing photosynthetic activity and primary
productiondue to the colouration of water in streams. Also the persisting nature of colour, non-biodegradable,
toxic and inhibitory nature of the spent dye bath has considerable deleterious effect on the total environmental
matrix[1].
Lablab purpureus(L.) , previously classified as Dolichos lablab(L.) is one of the major leguminous
forage and green manure crop in this area of the world[2]. Once the mature beans are harvested, they need only
be cooked to provide nourishment for humans[3] and [4]. Studies regarding value added traits such as bio-
functional and biologically active components of legumes have only recently begun because most speciality
phytochemicals are extracted from other plant sources. Not only can biofunctional legumes provide healthy food
constituents for use as nutraceuticals, pharmaceuticals and pesticides, but they can increase healthy food
resources worldwide.
II. Materials And Methods
Mat industry effluent was collected from Musiri, Trichy District, Tamilnadu. Lablab purpureus(L.)
seeds were collected from Agricultural seed farm, Trichy.ThePhysico-chemical characteristics of the effluent
and ground water like colour, odour, pH, electrical conductivity, biological oxygen demand [5], total dissolved
solids and total suspended solids[6], bicarbonate and carbonate [7], chloride[7], nitrate and
sulphate(turbidometric method), phenols were determined.
The effluent was then subjected to elemental analysis . Ground water was collected from respective
industry. Ground water treated plants were used as control and also used as a diluent.Biomolecules like total
soluble sugars [8],free aminoacids[9], total soluble starch[10], total soluble proteins[11], free proline[12], total
lipids of 15 and 30 day old plant leaves were analysed.
III. Statistical Analysis
The data recorded in the experiments were the mean values. The experiments were tested for significance
using ANOVA and Duncan multiple range test.
Effect Of Mat(Cyprus Rotundis) Industry Effluents On Biomolecules In Leaves Of Lablab…
DOI: 10.9790/2402-09112114116 www.iosrjournals.org 115 | Page
IV. Result And Discussion
Environmental problems in the present day world are myraid in number and pollution continues almost
unabated in developing countries in view of fastness of expansion of industries, factories, distilleries etc.
Physico-chemical analysis of effluent (Table 1) shows effluent from the mat industries is dark reddish brown
emanating an unpleasant odour. The pH is acidic with high values of EC(44.2 dsm-1
), BOD(59600 mg/l), total
suspended solids(14.597mg/l), total dissolved solids (28290 mg/l), carbonate (0.00 mg/l), bicarbonate(3020
mg/l), chloride(13322 mg/l), sulphate (1612.8 mg/l), nitrate(85.6 mg/l), phenols (0.19 mg/l) which are higher
than levels recommended by general standards for discharge of effluents on land for irrigation.
Elemental analysis (Table 2) such as zinc (12.48 mg/l), copper (5.25 mg/l), iron (18.45 mg/l), manganese (24.68
mg/l), lead(0.87 mg/l), mercury(0.15 mg/l), nickel(0.42 mg/l), chromium(1.26 mg/l), fluoride(0.50 mg/l),
sodium(7252 mg/l), potassium(49 mg/l),calcium(2388 mg/l), magnesium(1580 mg/l), which are higher than
general standards for discharge of effluents on land for irrigation. But cyanide which has 0.60 mg/l which is
lower than general standards for discharge of effluents on land for irrigation.
Table 1 Physico-Chemical Analysis Of Ground Water And Mat (Cyprus Rotundis) Industry Effluent
S1.N0. Physico-chemical characteristics Ground Water Effluent
1 Colour Colourless Dark-reddish brown
2 Odour Agreeable Unpleasant
3 PH 7.66 3.84
4 Electrical conductivity(dsm-1
) 1.75 44.2
5 Total suspended solids(mg/l) 192 14597
6 Total dissolved solids(mg/l) 1120 28290
7 BOD(mg/l) 75 59600
8 Carbonate(mg/l) Nil Nil
9 Bicarbonate(mg/l) 647 3020
10 Chloride(mg/l) 216 13322
11 Sulphate(mg/l) 79 1612.8
12 Nitrate(mg/l) 3.4 85.6
13 Phenols(mg/l) Nil 0.19
Table 2 Elemental Analysis Of Ground Water And Mat (Cyprus Rotundis) Industry Effluent
S1.No Elements Ground Water(mg/l) Effluent(mg/l)
1. Calcium 192 2388
2. Magnesium 122 1580
3. Sodium 163 7252
4. Potassium 20 49
5. Zinc 0.80 12.48
6. Copper 0.54 5.26
7. Iron 1.26 18.45
8. Manganese 0.68 24.68
9. Lead Nil 0.87
10. Nickel Nil 0.42
11. Chromium Nil 1.26
12 Fluoride Nil 0.5
13. Cyanide Nil 0.06
Table 3 Effect Of Mat(Cyprus Rotundis) Industry Effluents On Biomolecules In Leaves Of Lablab Purpureus(L.)
Sl.No. Biomolecules(mg/gdw) Plant (in
Days)
Effluent Treatment (%) ANOVA Source -
F Value0% 5% 10% 15% 25%
1 Total soluble sugar 15 87.33a
65.62b
58.43c
45.416d
36.19 A=523141**
B=1324081**
C=152177.9**
30 128.20 a
71.6 b
64.19 c
55.59 d
L
2 Total soluble starch 15 333.45 a
257.62 b
233.76 c
174.41 d
115.23 A=6.3E±07**
B=2.9E±08**
C=968080.2**
30 365.61v 286.71 b
254.71 c
213.51 d
L
3 Total lipids 15 10.66 a
9.08 b
8.01 c
7.66 d
4.33 A=6.445**
B=10.342**
C=0.084
30 14.86 a
13.66 b
10.25 c
8.73 d
L
4 Total soluble proteins 15 200 a
161 b
146 c
109 d
72 A=1045.333**
B=37473.333**
C=504.0000**
30 222 a
164 b
147 c
111 d
L
5 Free aminoacids 15 2.59 a
3.21 b
4.76 c
6.05 d
8.01 A=21218.778**
B=769519.2**
C=4622.630**
30 2.70 a
3.52 b
4.81 c
6.67 d
L
6 Free proline 15 0.02 a
0.27 b
0.37 c
0.65 d
0.80 A=856.655**
B=20399.276**
C=109.621**
30 0.03 a
0.35 b
0.40 c
0.75 d
L
Effect Of Mat(Cyprus Rotundis) Industry Effluents On Biomolecules In Leaves Of Lablab…
DOI: 10.9790/2402-09112114116 www.iosrjournals.org 116 | Page
Source of variation: A= age of the plant(df 1,24) ;B = effluent treatment(df 3,24); C = A * B (df 3, 24);
*significance at 5% level; ** significance at 1% level; a,b,c means within a row with same letters are not
significantly different from each other by Duncan Multiple Range Test, at 5% level; L= Lethal
Table 3 shows that the total soluble sugar, total soluble starch, total lipids , total soluble proteins, free
amino acids, proline differ significantly due to effluent treatment (0%, 5%, 10%, 15%) between age of the plant
(15th
and 30th
day). There is significant interaction between age of the plant and treatment.
It is observed that total soluble sugarof 15th
and 30th
day decreases at the rate of 2.659mg/g and
4.505mg/g dw of leaves respectively for each 5% of the effluent treatment.From the table 3, it is observed that
total soluble starch of 15th
and 30th
day old plant decreases at the rate of 10.020mg/g and 9.766mg/g dw of
leaves respectively for each 5% of the effluent treatment. Biomolecules like total soluble sugar, total soluble
starch, total lipids, total soluble proteins were decreased with increased effluent concentration may be due to the
presence of heavy metals and high BOD and COD.Similar observations were made by [13]. They reported that
cement klin dust, on entering into leaf tissues, the chemically active solution caused partial denaturations of the
chloroplasts and a decrease in pigment content in the cells of damaged leaves. Higher levels of cement klin dust
pollution considerably decreased the growth and metabolic activities.
From the table 3, it is observed that total lipidsof 15th
and 30th
day old plant decreases at the rate of
0.201mg/g dw and 0.436mg/g dw of leaves respectively for each 5% of the effluent.It is observed that total
soluble proteins of 15th
and 30th
day decreases at the rate of 5.760mg/g and 7.000mg/g dw of leaves
respectively for each 5% of the effluent treatment.Present observation on the reduction in total protein content in
effluent treated plants. Similar observations were made by [13]. They reported that reduction in protein content
in dusted plants parallel to that of many workers[14] ,[15], [16] thus appears that the total protein content is also
a suitable indicator of particulate pollution level.From the table 3, it is observed that free aminoacidsof 15th
and
30th
day old plant increases at the rate of0.239mg/g and 0.264mg/g dw of leaves respectively for each 5% of the
effluent treatment.Increase in free proline was observed with increasing effluent concentration in both 15 and 30
day . Also irrigation of crops and trees species such as maize, sorghum, black gram, cotton, acacia nilotica,
sesbaniarostrata affected further growth of seedlings/saplings at higher as well as moderate concentrations of
effluent.Free proline was the one to be increased maximally in most of the treated plants. The significance of
free proline is a moot point for discussion[17]. The accumulation of free proline is considered to be stress
tolerant marker [18], [19], [20], [21].
References
[1]. B.StephenInbaraj, K.Selvaraniand N.Sulochana, Evaluation of a carbonaceous sorbent prepared from [earl millet husks for its removal
of basic dyes, Journal of Scientific Industrial Research, 61, 2002, 971-978.
[2]. D.G. Cameron, Tropical and subtropical pasture legumes, Queensland Agricultural Journal, 1988, 110-113.
[3]. RV.Schaaffhausen, Dolichos lablab or Hyacinth Bean; Its uses for feed, food and soil improvement. Economic Botany.17:146-153,
1963a.
[4]. R.Sinclair, Dolichoslablab: una alternative para la alimentaciondelganado en epocas de verano. Centro internacional de informacion
Sorbe Cultivos de Cobertura(CIDICCO) Informe Tecnico No.15,1996.
[5]. APHA, Standard methods for examination of water and waste water ( 15th edition APHA, AWWAAA, WPCF, 1980).
[6]. Valentine Port, Laboratory analysis of common effluent plant(1-18, 1996).
[7]. P.R. Hesse, In: A Textbook of soil chemical analysis ( chemical publishing co, Inc New York, 1971).
[8]. M. Dubois, KN.Gilles, JK.Hamilton, PA. Rebers and F.Smith, Colorimetric method for determination of sugars and related substances,
Anal. Chem. 28: 1956,300-356.
[9]. W. Troll and K. Canan, A modified photometric ninhydrin method for the analysis of amino-iminoacids. J.Biol.Chem.200: 1953,803-
811.
[10]. RM. Mc cready, J.Guggolz, V.Silviera and HS.Owens, Determination of starch and amylose in vegetables, Anal. Chem., 22:
1950,1156.
[11]. OH. Lowry, NJ.Rosebrough, AL. Farr and RJ. Randall, Protein measurement with the folin phenol reagent, J.Bio.Chem. 193:
1951,265-275.
[12]. LS.Bates, RP.Waldron and ID. Teare, Rapid determination of free proline for water stress studies, Plt and Soil 39:1973, 205-207.
[13]. MSV.Prasad and JA. Inamdar, Effect of cement klin dust pollution on black gram (Vignamungo, Hepper). Proc.Indian.Acad.Sci(Plant
Sci) 100(6): 1990, 435-443.
[14]. BJ.Prasad, Phytotoxicity of refinery air pollutants, PhD thesis, Banaras Hindu University, Varanasi,1980.
[15]. M.Agarwal, A study of phytotoxicity of O3 and SO2 pollutants, PhD thesis, Banaras Hindu University, Varanasi. Agri. 10:1-42,1982.
[16]. K.Pawar, L.Trivedi and PS. Dudey, Comparative effects of cement coal dust and flyashabelmoschus; Int. J.Environ. Stud. 19:1982,
221-223.
[17]. D.Aspinall and LG. Paleg, Proline accumulation: Physiological aspects. In: Physiology and biochemistry of drought resistance in
plants Paleg ,Aspinal eds., (Academy press, New York , 1981)205-207.
[18]. RG.Wyn Jones and R.Storey ,Betaines: In: The Physiology and biochemistry of drought resistance in plants, 171-204, 1981.
[19]. RC. Johnson, HT. Nguyen and LI.Croy, Osmotic adjustment and solute accumulation in tow wheat genotypes differing in drought
resistance. Crop Sci. 24: 1984, 957-962.
[20]. PB. Naidu, GP. Jones, LG. Paleg and A. PoljakoffMayber, Proline analogues in Melaeuca species: responses ofmelaleucalanceolata
and M.uniculata to water stress and salinity. Aust. J.Plt.Physiol., 14: 1987,666-669.
[21]. M.Martin, F.Miceli, JA.Morgan and G. ScaletMandZerbi, Sythesis of osmotically active substances in winter wheat leaves as related
to drought resistance of different genotypes, J. Agron. Crop.Sci., 171: 1993,176-184.

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Effect Of Mat(Cyprus Rotundis) Industry Effluents On Biomolecules In Leaves Of Lablab Purpureus(L.)

  • 1. IOSR Journal of Environmental Science, Toxicology and Food Technology (IOSR-JESTFT) e-ISSN: 2319-2402,p- ISSN: 2319-2399.Volume 9, Issue 11 Ver. II (Nov. 2015), PP 114-116 www.iosrjournals.org DOI: 10.9790/2402-09112114116 www.iosrjournals.org 114 | Page Effect Of Mat(Cyprus Rotundis) Industry Effluents On Biomolecules In Leaves Of Lablab Purpureus(L.) Dr. C.Sumathy Assistant Professor In Biochemistry Department MIET Arts And Science College, Trichirapalli, Tamilnadu, India. Abstract: The effect of mat (Cyprus rotundis) industry effluent in different concentrations (viz. 5%, 10%, 15%, 25%, 30%, 35%, 40%, 45%, 50% ) on the biochemical constituents in leaves of Lablab purpureus(L.) was studied . Ground water treated plants were used as control and as well as diluent. Physico-chemical, Elemental analysis of effluent and ground water were also studied .Biochemical constituents like total soluble sugars, free aminoacids, total soluble starch, total soluble proteins,free proline, total lipids were decreased with increasing effluent concentration. Key words:- biochemical, constituents, diluent, effluent,physico-chemical. I. Introduction Water is a vital source for all kinds of life on planet; on the other hand, it is also a resource that is adversly affected both quantitatively and qualitatively due to urbanization , industrialization and other human activities. Even the ground water, which is supposed to be pure, is affected due to contamination of effluent discharged from industries containing decomposing matter and industrial wastes. So it becomes necessary to find out the level of pollution in water sources and examine if they are hazardous to plant.The mat industry is more than 250 years old. The woven mats are then polished with smooth river stones and their edges bound. While the superfine quality mats are fit enough to grace palaces and become part of a bridal troussea, the coarser ones are used all over Tamilnadu for sitting and sleeping, fancy wall fitting in cottages and hotels. Dyes contain metals such as copper, nickel, chromium, mercury and cobalt. In some dyes, these metals are integral to the dye's molecule; in others, they present as impurities. Metals are difficult to remove from waste water and may escape the capacities of the effluent treatment system. If the system manages to remove them, they become part of the sludge rendering it toxic. The coloured dye effluents are considered to be highly toxic to the aquatic biota and affect the symbiotic process by disturbing the natural equilibrium through reducing photosynthetic activity and primary productiondue to the colouration of water in streams. Also the persisting nature of colour, non-biodegradable, toxic and inhibitory nature of the spent dye bath has considerable deleterious effect on the total environmental matrix[1]. Lablab purpureus(L.) , previously classified as Dolichos lablab(L.) is one of the major leguminous forage and green manure crop in this area of the world[2]. Once the mature beans are harvested, they need only be cooked to provide nourishment for humans[3] and [4]. Studies regarding value added traits such as bio- functional and biologically active components of legumes have only recently begun because most speciality phytochemicals are extracted from other plant sources. Not only can biofunctional legumes provide healthy food constituents for use as nutraceuticals, pharmaceuticals and pesticides, but they can increase healthy food resources worldwide. II. Materials And Methods Mat industry effluent was collected from Musiri, Trichy District, Tamilnadu. Lablab purpureus(L.) seeds were collected from Agricultural seed farm, Trichy.ThePhysico-chemical characteristics of the effluent and ground water like colour, odour, pH, electrical conductivity, biological oxygen demand [5], total dissolved solids and total suspended solids[6], bicarbonate and carbonate [7], chloride[7], nitrate and sulphate(turbidometric method), phenols were determined. The effluent was then subjected to elemental analysis . Ground water was collected from respective industry. Ground water treated plants were used as control and also used as a diluent.Biomolecules like total soluble sugars [8],free aminoacids[9], total soluble starch[10], total soluble proteins[11], free proline[12], total lipids of 15 and 30 day old plant leaves were analysed. III. Statistical Analysis The data recorded in the experiments were the mean values. The experiments were tested for significance using ANOVA and Duncan multiple range test.
  • 2. Effect Of Mat(Cyprus Rotundis) Industry Effluents On Biomolecules In Leaves Of Lablab… DOI: 10.9790/2402-09112114116 www.iosrjournals.org 115 | Page IV. Result And Discussion Environmental problems in the present day world are myraid in number and pollution continues almost unabated in developing countries in view of fastness of expansion of industries, factories, distilleries etc. Physico-chemical analysis of effluent (Table 1) shows effluent from the mat industries is dark reddish brown emanating an unpleasant odour. The pH is acidic with high values of EC(44.2 dsm-1 ), BOD(59600 mg/l), total suspended solids(14.597mg/l), total dissolved solids (28290 mg/l), carbonate (0.00 mg/l), bicarbonate(3020 mg/l), chloride(13322 mg/l), sulphate (1612.8 mg/l), nitrate(85.6 mg/l), phenols (0.19 mg/l) which are higher than levels recommended by general standards for discharge of effluents on land for irrigation. Elemental analysis (Table 2) such as zinc (12.48 mg/l), copper (5.25 mg/l), iron (18.45 mg/l), manganese (24.68 mg/l), lead(0.87 mg/l), mercury(0.15 mg/l), nickel(0.42 mg/l), chromium(1.26 mg/l), fluoride(0.50 mg/l), sodium(7252 mg/l), potassium(49 mg/l),calcium(2388 mg/l), magnesium(1580 mg/l), which are higher than general standards for discharge of effluents on land for irrigation. But cyanide which has 0.60 mg/l which is lower than general standards for discharge of effluents on land for irrigation. Table 1 Physico-Chemical Analysis Of Ground Water And Mat (Cyprus Rotundis) Industry Effluent S1.N0. Physico-chemical characteristics Ground Water Effluent 1 Colour Colourless Dark-reddish brown 2 Odour Agreeable Unpleasant 3 PH 7.66 3.84 4 Electrical conductivity(dsm-1 ) 1.75 44.2 5 Total suspended solids(mg/l) 192 14597 6 Total dissolved solids(mg/l) 1120 28290 7 BOD(mg/l) 75 59600 8 Carbonate(mg/l) Nil Nil 9 Bicarbonate(mg/l) 647 3020 10 Chloride(mg/l) 216 13322 11 Sulphate(mg/l) 79 1612.8 12 Nitrate(mg/l) 3.4 85.6 13 Phenols(mg/l) Nil 0.19 Table 2 Elemental Analysis Of Ground Water And Mat (Cyprus Rotundis) Industry Effluent S1.No Elements Ground Water(mg/l) Effluent(mg/l) 1. Calcium 192 2388 2. Magnesium 122 1580 3. Sodium 163 7252 4. Potassium 20 49 5. Zinc 0.80 12.48 6. Copper 0.54 5.26 7. Iron 1.26 18.45 8. Manganese 0.68 24.68 9. Lead Nil 0.87 10. Nickel Nil 0.42 11. Chromium Nil 1.26 12 Fluoride Nil 0.5 13. Cyanide Nil 0.06 Table 3 Effect Of Mat(Cyprus Rotundis) Industry Effluents On Biomolecules In Leaves Of Lablab Purpureus(L.) Sl.No. Biomolecules(mg/gdw) Plant (in Days) Effluent Treatment (%) ANOVA Source - F Value0% 5% 10% 15% 25% 1 Total soluble sugar 15 87.33a 65.62b 58.43c 45.416d 36.19 A=523141** B=1324081** C=152177.9** 30 128.20 a 71.6 b 64.19 c 55.59 d L 2 Total soluble starch 15 333.45 a 257.62 b 233.76 c 174.41 d 115.23 A=6.3E±07** B=2.9E±08** C=968080.2** 30 365.61v 286.71 b 254.71 c 213.51 d L 3 Total lipids 15 10.66 a 9.08 b 8.01 c 7.66 d 4.33 A=6.445** B=10.342** C=0.084 30 14.86 a 13.66 b 10.25 c 8.73 d L 4 Total soluble proteins 15 200 a 161 b 146 c 109 d 72 A=1045.333** B=37473.333** C=504.0000** 30 222 a 164 b 147 c 111 d L 5 Free aminoacids 15 2.59 a 3.21 b 4.76 c 6.05 d 8.01 A=21218.778** B=769519.2** C=4622.630** 30 2.70 a 3.52 b 4.81 c 6.67 d L 6 Free proline 15 0.02 a 0.27 b 0.37 c 0.65 d 0.80 A=856.655** B=20399.276** C=109.621** 30 0.03 a 0.35 b 0.40 c 0.75 d L
  • 3. Effect Of Mat(Cyprus Rotundis) Industry Effluents On Biomolecules In Leaves Of Lablab… DOI: 10.9790/2402-09112114116 www.iosrjournals.org 116 | Page Source of variation: A= age of the plant(df 1,24) ;B = effluent treatment(df 3,24); C = A * B (df 3, 24); *significance at 5% level; ** significance at 1% level; a,b,c means within a row with same letters are not significantly different from each other by Duncan Multiple Range Test, at 5% level; L= Lethal Table 3 shows that the total soluble sugar, total soluble starch, total lipids , total soluble proteins, free amino acids, proline differ significantly due to effluent treatment (0%, 5%, 10%, 15%) between age of the plant (15th and 30th day). There is significant interaction between age of the plant and treatment. It is observed that total soluble sugarof 15th and 30th day decreases at the rate of 2.659mg/g and 4.505mg/g dw of leaves respectively for each 5% of the effluent treatment.From the table 3, it is observed that total soluble starch of 15th and 30th day old plant decreases at the rate of 10.020mg/g and 9.766mg/g dw of leaves respectively for each 5% of the effluent treatment. Biomolecules like total soluble sugar, total soluble starch, total lipids, total soluble proteins were decreased with increased effluent concentration may be due to the presence of heavy metals and high BOD and COD.Similar observations were made by [13]. They reported that cement klin dust, on entering into leaf tissues, the chemically active solution caused partial denaturations of the chloroplasts and a decrease in pigment content in the cells of damaged leaves. Higher levels of cement klin dust pollution considerably decreased the growth and metabolic activities. From the table 3, it is observed that total lipidsof 15th and 30th day old plant decreases at the rate of 0.201mg/g dw and 0.436mg/g dw of leaves respectively for each 5% of the effluent.It is observed that total soluble proteins of 15th and 30th day decreases at the rate of 5.760mg/g and 7.000mg/g dw of leaves respectively for each 5% of the effluent treatment.Present observation on the reduction in total protein content in effluent treated plants. Similar observations were made by [13]. They reported that reduction in protein content in dusted plants parallel to that of many workers[14] ,[15], [16] thus appears that the total protein content is also a suitable indicator of particulate pollution level.From the table 3, it is observed that free aminoacidsof 15th and 30th day old plant increases at the rate of0.239mg/g and 0.264mg/g dw of leaves respectively for each 5% of the effluent treatment.Increase in free proline was observed with increasing effluent concentration in both 15 and 30 day . Also irrigation of crops and trees species such as maize, sorghum, black gram, cotton, acacia nilotica, sesbaniarostrata affected further growth of seedlings/saplings at higher as well as moderate concentrations of effluent.Free proline was the one to be increased maximally in most of the treated plants. The significance of free proline is a moot point for discussion[17]. The accumulation of free proline is considered to be stress tolerant marker [18], [19], [20], [21]. References [1]. B.StephenInbaraj, K.Selvaraniand N.Sulochana, Evaluation of a carbonaceous sorbent prepared from [earl millet husks for its removal of basic dyes, Journal of Scientific Industrial Research, 61, 2002, 971-978. [2]. D.G. Cameron, Tropical and subtropical pasture legumes, Queensland Agricultural Journal, 1988, 110-113. [3]. RV.Schaaffhausen, Dolichos lablab or Hyacinth Bean; Its uses for feed, food and soil improvement. Economic Botany.17:146-153, 1963a. [4]. R.Sinclair, Dolichoslablab: una alternative para la alimentaciondelganado en epocas de verano. Centro internacional de informacion Sorbe Cultivos de Cobertura(CIDICCO) Informe Tecnico No.15,1996. [5]. APHA, Standard methods for examination of water and waste water ( 15th edition APHA, AWWAAA, WPCF, 1980). [6]. Valentine Port, Laboratory analysis of common effluent plant(1-18, 1996). [7]. P.R. Hesse, In: A Textbook of soil chemical analysis ( chemical publishing co, Inc New York, 1971). [8]. M. Dubois, KN.Gilles, JK.Hamilton, PA. Rebers and F.Smith, Colorimetric method for determination of sugars and related substances, Anal. Chem. 28: 1956,300-356. [9]. W. Troll and K. Canan, A modified photometric ninhydrin method for the analysis of amino-iminoacids. J.Biol.Chem.200: 1953,803- 811. [10]. RM. Mc cready, J.Guggolz, V.Silviera and HS.Owens, Determination of starch and amylose in vegetables, Anal. Chem., 22: 1950,1156. [11]. OH. Lowry, NJ.Rosebrough, AL. Farr and RJ. Randall, Protein measurement with the folin phenol reagent, J.Bio.Chem. 193: 1951,265-275. [12]. LS.Bates, RP.Waldron and ID. Teare, Rapid determination of free proline for water stress studies, Plt and Soil 39:1973, 205-207. [13]. MSV.Prasad and JA. Inamdar, Effect of cement klin dust pollution on black gram (Vignamungo, Hepper). Proc.Indian.Acad.Sci(Plant Sci) 100(6): 1990, 435-443. [14]. BJ.Prasad, Phytotoxicity of refinery air pollutants, PhD thesis, Banaras Hindu University, Varanasi,1980. [15]. M.Agarwal, A study of phytotoxicity of O3 and SO2 pollutants, PhD thesis, Banaras Hindu University, Varanasi. Agri. 10:1-42,1982. [16]. K.Pawar, L.Trivedi and PS. Dudey, Comparative effects of cement coal dust and flyashabelmoschus; Int. J.Environ. Stud. 19:1982, 221-223. [17]. D.Aspinall and LG. Paleg, Proline accumulation: Physiological aspects. In: Physiology and biochemistry of drought resistance in plants Paleg ,Aspinal eds., (Academy press, New York , 1981)205-207. [18]. RG.Wyn Jones and R.Storey ,Betaines: In: The Physiology and biochemistry of drought resistance in plants, 171-204, 1981. [19]. RC. Johnson, HT. Nguyen and LI.Croy, Osmotic adjustment and solute accumulation in tow wheat genotypes differing in drought resistance. Crop Sci. 24: 1984, 957-962. [20]. PB. Naidu, GP. Jones, LG. Paleg and A. PoljakoffMayber, Proline analogues in Melaeuca species: responses ofmelaleucalanceolata and M.uniculata to water stress and salinity. Aust. J.Plt.Physiol., 14: 1987,666-669. [21]. M.Martin, F.Miceli, JA.Morgan and G. ScaletMandZerbi, Sythesis of osmotically active substances in winter wheat leaves as related to drought resistance of different genotypes, J. Agron. Crop.Sci., 171: 1993,176-184.