Much (32-84%) of the ground water surveyed in different Indian States
is rated either saline or alkali. Because of the continental monsoonal
climate, the basic principles of saline water management need some ad
aptation, e.g. providing for a leaching requirement is not appropriate
when the growing season for post-monsoon winter crops starts with a s
urface-leached soil profile, because it would increase the salt load.
High salinities during the initial stages of growth are particularly h
armful. Further, if benefits are to be gained from frequent saline irr
igation, the amount of water applied per irrigation needs to be reduce
d. This is not possible with most widely practiced surface irrigation
methods, but can be achieved with sprinkler and drip methods. However,
in India the large-scale use of such systems is not yet technically o
r economically feasible. Another management goal is simultaneously to
encourage the utilisation of carried over rainwater in the soil profil
e/shallow watertables. Tolerance limits of crops to the use of saline
water in different agro-ecological regions of India are available, and
have been observed to vary with soil type, rainfall and anionic/catio
nic constituents of salinity. Multi-location trials on the appropriate
use of saline and non-saline water reveal the benefits of irrigating
with non-saline canal water during the initial stages of growth, as we
ll as cycles of saline and non-saline water during the pre-sowing irri
gation period. Monsoon-induced salt leaching decreases with increasing
clay content, SAR(iw), and is enhanced with increasing chloride salin
ity. Additional doses of phosphorous to alleviate the effects of chlor
ide toxicity, and the use of organic materials to enhance the efficien
cy of applied nitrogen are recommended under saline-irrigated conditio
ns. Contrary to the general belief that soils irrigated with high-SAR
saline water may regain their infiltration capacity when the electroly
tic concentration of ingoing water is greater than the flocculation va
lue, irreversible reductions are induced under cyclic saline-rainwater
infiltration where sub-soil layers, ingressed with clays from the plo
ugh layer, control steady intake rates. Thus, the use of gypsum (SAR(i
w) > 20) is advocated. Gypsum is also needed for soils irrigated with
saline water with an Mg:Ca ratio > 3 and rich in silica. Other cultura
l practices, such as furrow planting, increasing the plant density and
post-seeding irrigation in crops like mustard, also prove useful. Wat
er-quality standards which were too conservative have been replaced by
site-specific guidelines where factors such as soil texture, rainfall
and crop tolerance have been given due consideration.