The
total consumption of chemical fertilizers is in increasing trends from 0.69 lakh tonnes in
1950-51 to 173.18 lakh tonnes in 1997-98. Decreasing trends in total fertilizers
consumption is observed from 127.28 lakh tonnes in 1991-92 to 121.55 lakh tonnes in
1992-93. The same decreasing trend is observed in Phosphatic and Potassic fertilizer
consumption during the same period. In case of nitrogenous fertilizers, continuous
increasing trends is observed from 1950-51 to 1997-98. Fertilizer consumption per hectare
was negligible (0.5 kg per hectare) in 1951-52 increased to 76.75 kgs per hectare during
1996-97.
Table-2A : Consumption of pesticides (technical grade material)
(in thousand tonnes)
Year
|
Pesticides
|
1950-51
|
2.35
|
1960-61
|
8.62
|
1970-71
|
24.32
|
1980-81
|
45.00
|
1988-89
|
75.89
|
The trend in consumption of pesticide is increasing from 2.35 thousand tonnes to 75.8
thousand tonnes from 1950-51 to 1988-89.
Table:
2B Trends in consumption pattern of different groups of pesticides
(Technical
Grade Material, MT)
Year |
Insecticides |
Fungicides |
Herbicides |
Others |
Total |
1988 |
67692
|
16365
|
4160
|
1020
|
89237
|
1989 |
56424
|
17530
|
4730
|
925
|
79609
|
1990 |
47074
|
17770
|
5162
|
1075
|
71081
|
1991 |
49516
|
18465
|
5367
|
975
|
74323
|
1992 |
55166
|
18925
|
6695
|
1280
|
82066
|
1993 |
56239
|
17313
|
9975
|
1315
|
84842
|
1994 |
55209
|
16956
|
10798
|
1315
|
84278
|
1995 |
59487
|
19197
|
10557
|
1345
|
90586
|
1996 |
38111
|
20795
|
10651
|
1625
|
71182
|
1997 |
37602
|
21695
|
11869
|
1725
|
72891
|
| Compound Growth Rates (%) |
|
|
|
1998-95 |
-0.44
|
1.07
|
16.52
|
5.59
|
1.22
|
1995-97 |
-20.49
|
6.31
|
6.03
|
13.25
|
-10.30
|
1988-97
|
-3.88
|
2.31
|
13.70
|
6.71
|
-0.59
|
Source: Various issues of pesticides information (PAI)
Pesticide usage:
Herbicides:
The
use of herbicides has gradually improved in the country. During the period 1988 to 1997
herbicides had an annual growth rate 13.70 percent. The share of herbicides in total
pesticides consumption has increased from 4.7 percent in 1988 to 16.3 percent 1997. The
used of herbicides is increasing in agriculturally in advanced regions of the country due
to rising cost of labour and shift of labour from agriculture to other investors. Nearly,
85 percent of herbicides are used on rice, tea, bee and beans (BAMI 1996).
Insecticides:
India
is predominantly an insecticides market. The most important crops with regard to
insecticide usage are cotton and rice which account for about 70 percent of total
pesticide consumption in India. During the last 10 year (1988-97), the consumption of
insecticide has declined an annual compound growth rate of 3.88 percent. Organo phosphates
dominate the Indian market with about 50 percent share followed by the synthetic
pyrephroids(19 percent), organo chlorines (18 percent), carbamats (4 percent) and
bio-pesticides(1 percent). While organo chlorine group of pesticides has been banned and
phased out in advanced countries, India still uses some of this products with adverse
impact on environmental and human health (BAMI 1996).
Fungicides:
At present, fungicides most commonly used agro-chemicals
for growing food crops and vegetables. In India the use of fungicides is most popular in
fruits followed by potatoe, rice, tea and coffee. The use of fungicides has increased
significantly (2.31 percent) during 1988-97 and its share in total pesticide consumption
has increased from about 18 percent to about 30 percent.
PROBLEM POSED BY FERTILIZERS AND PESTICIDES
Fertilizers:
Continuous
use of inorganic fertilizers mainly containing major nutrients NPK in large quantities and
neglecting organic and bio-fertilizers paved the way for deterioration of soil health and
in turn ill effects on plants, human being and cattle.
The adverse
effects of using fertilizers are explained below.
I Nitrate
pollution:
Nitrogen
is applied to the soil as urea (Which is readily hydrolyzed to ammonium), ammonium nitrate
or a combination of ammonium and nitrate. About 40-60 percent of applied nitrogen is lost
by voltalization run off, de-nitrification and leaching. The nitrate that is leached
causes a lot of visible and invisible hazardous effects.
Visible effects :
Plants
become succulent and dark green colour thus becoming more susceptible to pests and
diseases. Ex. BPH in paddy in most of the paddy growing regions.
It
increases the growth, weakens the stem and brings lodging in crops like paddy. It reduces
the quality of the seed
Invisible effects:
Pollution of ground water by nitrates : Excess nitrate moves below
the root zone or into the ground water (once the ground water becoming polluted it
remaining for extended periods of time) and draining of such water causes or disease
called "Methemoglobinemia", where nitrite
(reduced form of nitrate) interferes with oxygen carrying capacity of blood.
Japanese encephalitis (JE) : Excess use of urea in rice fields
promotes the growth and spread of vectors causing of human disease called JE. Children
between the age group between 4-14 years are mainly affected.
Nitrosomine illness is caused by the presence of secondary amines
which causes cancer in human beings.
Feroxyl
nitrates, alkyl nitrates, vapours of HNO3 and nitrate aerosoles causes respiratory illness
HNO3
in aerosols may lead to acid rains causing lot of damage to
ecosystem and buildings
Nitrate
oxide produced by de-nitrification damages the stratospheric ozone
layer.
- Eutrophication:
This refers to the process of enrichment of surface water bodies with nutrients, addition
of plant nutrients particularly P&N to surface water bodies such as lakes, reservoirs
and streams result in intense prolification and accumulation of algae and higher aquatic
plants in excessive quantities which can result in detrimental changes in water quality
and can significantly interfere with mans use of the water resource.
- Soil
acidification and alkalization:
Development of soil acidification and alkalization due to continuos use of acidic (NH4
Cl (NH2 ) SO4 etc.) and basic (NANO3 ) (CAN basic
slag etc.) fertilizers causing imbalance in nutrients availability to crops and effecting
activities of beneficial micro organisms.
Iron, aluminium and manganese toxicities in acidic soil and sodium
toxicity in alkali soils effect the availability of other nutrients and deteriorate
fertility and productivity of soils.
The
continuous application of P fertilizers can
result in the build up of trace metal contaminants such as arsenic and cadmium contained
in the fertilize.
Excessive
application of potassic fertilizers decrease vit
"C" (ascorbic acid) and carotene content in vegetable and fruits.
.
Excessive application of chemical fertilizers lead to
malnutrition due to degradation of carbohydrates and proteins both qualitatively and
quantitatively.
.
Excessive application of chemical fertilizers effects
physical properties of soil such as infiltration, soil aeration, soil structure and bulk
density etc.
Pesticides:
Pesticides
enter environment mainly by air, water and soil. Pesticides enter air by sprayed drift or
voltalization from soil or water. The entry of pesticides in water is mainly by surface
runoff, sediment transport from treated soil, industrial wastes and direct application of
pesticides to control acquatic pests. Soil receives pesticides when the pesticides are
directly applied besides runoff from plants, rains and dumping of empty containers of
pesticides. The challenges posed by pesticide usage are explained below:
Indiscriminate
and defective handling of the pesticides causes environmental
pollution and leads to health hazardous.
Pesticides resistance: Consistent use of pesticide to control pests
had led to development of resistance among pests and vectors and adverse effect on non
target organisms.
Destruction of beneficial organisms: Continuous use of pesticides
had an adverse effect on beneficial organisms like honeybees, pollinators, parasites and
predators. At the height of the American boll worm problem in Guntur and Prakasham
districts in Andhra Pradesh in 1986 almost all the predaceous bird fauna were totally
exterminated. The crisis in cotton cultivation posed by boll worms, white flies etc.
leading to total crop loss and eventual frustration and suicides of many farmers in A.P.
Pesticides poisoning:
a.
Manufacturing Level: Persons engaged in manufacturing of insecticides are subjected
to insecticider exposure. This results in chronic poisoning. The poisoning symptoms of
aldrin, dialdrin and endrine are headache, fatigue, loss of appetite, loss of weight and
memory.
Operating
level: The majority of cases occur in hot and humid field conditions. The reason is
that the operators or farmers do not wear protective clothing.
Consumer
level: Chlorinated hydro carbons can accumulate in the adipose tissues of man. It is
very difficult to ascertain the extent of safety of residue in human beings. However,
there are a number of evidences that some forms of wild life are suffering due to
bio-magnification of these residues.
VI. Pesticide residues:
The
widespread use of pesticides provides many possible sources of pesticides in the
environment and living organism. Pesticides after application are known to persist on crop
produce, soil, water and air with harmful effects on human health and the environment. In
India problem of pesticide residue in food has been studied by Indian Council of Medical
Research (ICMR), Indian Council of Agricultural Research (ICAR) and other institutions in
an isolated manner.
PESTICIDES RESIDUES IN WATER
|
SAMPLING
AREA
|
PESTICIDE
|
RESIDUE
LEVEL
|
1
|
Ponds in coffee plantations,
Chikmagalore, Karnataka
|
HCH
|
0.02
0.2 ppm
|
2
|
Yamuna, Delhi
|
DDT
|
2.9
21.8 ppm
|
3
|
Srinagar, J & K
|
HCH
|
2.5
73.5 ppm
|
4
|
River Khan, near Indore,
M.P.
|
Total HCH
|
0.05
0.39 ppm
|
5
|
River Chambal, near Kota,
Rajasthan
|
Total HCH
|
0.06
1.49 ppm
|
6
|
Drinking water source around
Bhopal
|
Total HCH
|
1.58-15.88
ppm
|
|
|
|
3.15-34.77
ppm
|
Source : Handa and Walia (1996)
DDT CONTAMINATION IN MILK
| STATE |
TOTAL SAMPLES |
INCIDENCE(%) |
SAMPLE ABOVE TOLERANCE LEVEL(%) |
RANGE(ppm) |
| Punjab |
263
|
97.7
|
50.6
|
ND-1.11
|
| Haryana |
120
|
93.7
|
05.0
|
ND-0.33
|
| Himachal Pradesh |
120
|
100.0
|
55.8
|
0.006-0.75
|
| Uttar Pradesh |
240
|
57.1
|
10.8
|
ND-0.652
|
| Madhya Pradesh |
240
|
95.8
|
21.7
|
ND-0.36
|
| Maharashtra |
299
|
100.0
|
74.2
|
0.02-0.965
|
| Gujarat |
120
|
100.0
|
70.0
|
0.015-0.20
|
| Andhra Pradesh |
240
|
96.7
|
57.1
|
ND-2.224
|
| Karnataka |
203
|
22.2
|
17.7
|
ND-1.079
|
| Kerala |
120
|
95.8
|
09.2
|
ND-0.08
|
| Bihar |
120
|
95.8
|
19.2
|
ND-0.08
|
| West Bengal |
120
|
35.8
|
12.5
|
ND-2.82
|
| All states of India |
2205
|
81.1
|
36.0
|
ND-2.224
|
Source : ICAR PROJECT 1986 - 1999
VALUES
FOR DDT AND BHC IN HUMAN MILK
COUNTRY
|
YEAR
|
BHC
|
DDT
|
Japan
|
1977
|
250
|
1900
|
USA
|
1977-78
|
NA
|
NA
|
Canada
|
1987
|
34
|
840
|
Great Britain
|
1979-80
|
220
|
1900
|
Germany
|
1979-81
|
450
|
1900
|
Italy
|
1985
|
7
|
47
|
Israel
|
1985
|
390
|
2800
|
Kenya
|
1983-85
|
110
|
6900
|
China
|
1982
|
6600
|
6200
|
India
|
1988-89
|
750
|
3700
|
Figure by which overall intake exceeds the acceptable daily in take (ADI), based on 2 %
fat 0.8 litres of milk per day.
Source : Ho1. E.H.1995 Down
to Earth. 4(10). 27-31
6. Destruction of soil
microbes spoiling the soil health.
- Minor pests become major ones
- Increase in investment for
crop production
- Severe imbalance in ecology
Herbicides:
1. Persistence in soil: The herbicide applied to one crop may persist
in the soil at concentration high enough to damage subsequent sensitive crops.
2. Residues in crops: At coimbatore, the sorghum grain & stalk
showed detectable amount of residues when atrazine was applied at 0.5 and 1.0 Kg / ha
which was well below the MRL.
3. Toxicity: Herbicides like trifluralin were found associated with
nitrosamines which are potent carcinogens. However, at 1.12 kg/ha of trifluralin, the top
soil layer (15 cm) would contain only 0.006 ppb of nitrosamine and this is too small
amount to cause cancer (Witter, 1980).
Fungicides:
Emergence of resistant strains: Improper use of systematic
fungicides like (carbendazium) resulted into development of resistant stains of different
plant pathogens.
Health Hazards: Maneb and Streptocycline caused dermititis and some
people working with captan or in fields treated with it showed symptoms of skin irritation
and rashes (Sharma Kaur 1990).
Fungicide residues: If the fungicides are used judiciously they may
pose serious residue problems.
Non-target effects: Copper fungicides used for the control of
coffee rust resulted in increased occurrence of coffee leaf miner and of spider mites
(Panlam et al 1976)
Beever
et al (1984) reported that the residues of captan when used as spray against Botrytis
storage of kiwi fruit were within the acceptable limits when used as per recommended dose.
However, the increased number of sprays resulted in more than acceptable limit of residue
levels.
STRATEGIES
TO OVERCOME THE CHALLENGES OF PRESENT SITUATION:
After
seeing the deleterious effects arising with the use of agro chemicals coupled with the
degradation of cultivable land and increasing agricultural pollution has created an
unhealthy situation in the country. In order to balance this situation, organic farming,
which aims at cultivating the land and raising crops in such a way as to keep the soil
alive and in good health may be an alternative to the present system of farming solely
depending on chemicals.
It
is a method of farming which avoids or largely excludes the use of compound chemicals such
as chemical fertilizers, pesticides and herbicides. Instead of that natural resources such
as organic matters, minerals and microbes are used. It gives an idea to use all sources
which are natural so that soil health is maintained.
Organic
farming systems rely on large scale application of animal or FYM, compost, crop rotations,
cooperative residues, green manuring, vermicompost, bio-fertilizers, bio-pesticides and
biological control.
Key
characteristics:
Weed,
disease and pest control relying primarily on crop rotations, natural predators,
diversity, organic manuring, resistant varieties and limited (preferably minimal) thermal,
biological and chemical intervention;
The
extensive management of livestock, paying full regard to their evolutionary adaptations,
behavioural needs and animal welfare issues with respect to nutrition, housing, health,
breeding and rearing;
- Careful attention to the
impact of the farming system on the wider environment and the conservation of wildlife and
natural habitats.
ALTERNATIVES
FOR CHEMICAL FERTILIZERS
In
India the use of organic manures in subsistence forming is an age old practice. Organic
manures improve physical, chemical and biological properties of the soil. Addition of
organic manure improves structure aeration, water holding capacity of soils, reduces
phosphorous fixation in acidic soil forms chilates with metallic ions and reduces their
toxicity in crops. For substituting the chemical fertilizers various forms of organic
manures and bio-fertilizers are explained below:
FYM cow dung is an important source of pl. nutrients. FYM is
composed of drug, urine, bedding and straw. FYM contains approximately 5-6 Kg N, 1.5-2 Kg
phosphorus and 5-6 Kg potash/ ton. It builds up soil health considerably.
Green Manuring: It is considered a good source of N and
it increases the availability of P, K and secondary and trace elements to the soil.
Coir Pith: The annual production of coir pith in India is about 7.5
million tonnes. Preferably bio-degraded and amended coir pith can serve as a substitute
for FYM or similar organic manure, plenrotus sojorcaju. As per gillus and Trechoderma are
found to be potent degrading of coir pith.
Vermicompost: is 5 times richer in N, 7 times in P, 11 times in K,
2 times in Mg, 2 times in Ca & 7 times in actinomy and than ordinary soil. It is a
rich source of vitamins and growth hormones like gibberling which regulate the growth of
plant and microbes. The compost prepared by using earth wiring is called vermi-compost.
Biofertilizers: These are living cells of different types of micro
organisms which have an ability to mobilize nutritionally important elements from non
usable to usable form. They influence the avalability of major nutrients like nitrogen,
phosphorus, potassium and sulphur to the plants. Rhizobium, Azotobacter, Azospirillum,
Blue green algae, Azolla, Mycorrhizae, phosphate solubilizing bacteria can be used as
biofertilizers to increase the crop production. These micro organisms require organic
matter for their growth and activity in the soil and provide valuable nutrients to the
plants in the soil.
Pesticides:
Many
of the pesticide applications may be unnecessary and are economically unsound. A range of
alternative methods of pest control to be used inorganic farming are detailed below:
- Deep ploughing the fields
during summer season help in killing pests, larval & eggs.
- Clean cultivation by
destruction of weeds and other alternate hosts breaks the carry over of the pest in
succession which considerably reduces the pest numbers.
- Adopting crop rotations to
avoid carry over of pests from one season to next season.
- Change in time of sowing
- Draining of water out of
fields at times of pests growing in number
- Use of resistant varieties
- Growing of trap crops
- Release of parasites and
predators
- Use of pheromone traps and
light traps
- Use of biological
insecticides
- Use of mechanical weed
control
- Cover cropping to control
weed-seed germination
CONCLUSION:
Organic
agriculture is a viable alternative because it enlivens the soil, strengthens the natural
resource base and sustains biological production at levels to commensurate the carrying
capacity of the managed agro eco-system. In addition to this export market can also be
tapped by group initiatives in organic farming. In a country like India, food production
has to grow steadily. A sudden switch over to organic farming is not feasible. The minimum
food requirement for the year 2001 is 240 million tonnes. The stage will be set in due
course for a smooth transition to organic farming without causing any decline in
production. The efforts from extension, research, supply of inputs, development of market
channels, for disposal of organic foods are needed to facilitate the successful adoption
of organic farming by the farmers. The approach shall be farmer centred and the programmes
developed shall create conditions for the conservation and efficient use of locally
available resources as inputs in agriculture. The role of MANAGE will be taking up
specialized programmes in organic farming for training of extension personnels.