- •Unit 1. Lesson1.
- •Vocabulary:
- •Lesson 2
- •1.Прочитайте и переведите текст. Water is life.
- •Vocabulary:
- •Lesson 3
- •1.Прочитайте и переведите текст. The hydrologic cycle.
- •Lesson 4.
- •1.Прочитайте и переведите текст. The water of the Earth
- •Lesson 5.
- •1. Прочитайте и переведите текст. Hydraulics.
- •Vocabulary:
- •Lesson 6.
- •1.Прочитайте и переведите текст.
- •Vocabulary:
- •Lesson 7.
- •1.Прочитайте и переведите текст. Water in Moscow.
- •Vocabulary:
- •Lesson 8.
- •1. Прочитайте и переведите текст. The spring water of Moscow
- •Vocabulary:
- •Lesson 9.
- •Прочитайте и переведите текст. Moscow waterworks.
- •Vocabulary:
- •Lesson 10.
- •1.Прочитайте и переведите текст Where Moscow’s water flows from
- •Vocabulary:
- •Lesson 11.
- •1.Прочитайте и переведите текст. Water: Pay More, Use Less.
- •Vocabulary:
- •Lessons 12-13.
- •1. Прочитайте и переведите текст.
- •Part 1.
- •Vocabulary:
- •Vocabulary:
- •Lessons 14-15. Water Supply and sewages
- •1.Прочитайте и переведите текст.
- •Vocabulary:
- •Part 4 .
- •Vocabulary:
- •Lesson16.
- •1.Прочитайте и переведите текст. How can the Aral Sea be saved?
- •Vocabulary:
- •Lesson 17.
- •1.Прочитайте и переведите текст. Keeping the Caspian clean.
- •Vocabulary:
- •Lesson 18.
- •1.Прочитайте и переведите текст. What is to be done with the Sea of Azov.
- •Vocabulary:
- •Lesson 19.
- •1. Прочитайте и переведите текст.
- •Volga water is not sufficient
- •Lesson 20.
- •1. Прочитайте и переведите текст. Watching the ecology.
- •Text 2 Sprinkler irrigation
- •Text 3 Subirrigation
- •Text 1 The perspective and objectives of irrigation
- •Irrigation methods and their selection
- •2.1 Compatibility
- •2.3.Topographical characteristics
- •2.4. Soils
- •2.5. Water supply
- •2.6.Crops
- •2.7. Social influences
- •2.8. External influences
- •2.9. Summary
- •3.1.2 Scope of the guide
- •3.1.3 Evolution of the practice
- •3.2 Surface irrigation methods
- •3.2.1 Basin irrigation
- •3.2.2 Border irrigation
- •3.2.4 Uncontrolled flooding
- •3.3 Requirements for optimal performance
- •3.3.1 Inlet discharge control
- •3.3.2 Wastewater recovery and reuse
- •3.4 Surface irrigation structures
- •3.4.1 Diversion structures
- •3.4.2 Conveyance, distribution and management structures
- •3.4.3 Field distribution systems
- •Text 4 Advantages and disadvantages of surface irrigation
- •4.1. Advantages
- •4.2. Disadvantages
- •Text 5.
- •5.1.Objective and scope of design
- •5.2 The basic design process
- •5.2.1. Preliminary design
- •5.2.2 Detailed design
- •5.3 Computation of advance and intake opportunity time
- •5.4 Furrow irrigation flow rates, cutoff times, and field layouts
- •5.4.1 Furrow design procedure for systems without cutback or reuse
- •5.4.2 Design procedure for furrow cutback systems
- •5.4.3 Design of furrow systems with tailwater reuse
- •5.4.4 Furrow irrigation design examples
- •5.5 Border irrigation design
- •5.5.1 Design of open-end border systems
- •5.5.2 Design of blocked-end borders
- •5.5.4 A blocked-end border design example
- •5.7 Summary
- •5.6 Basin irrigation design
- •5.6.1 An example of basin design
- •Text 6. Field measurements
- •Text 7. Determining water requirements
- •Figure 2 a perspective of the on-farm water balance
- •Figure3 The perspective of water balance at the field level
- •An example problem on soil moisture
- •Text 2 Environmental problems
- •Text 3 Aral Sea- What Was and What Is
- •Is the climate warming?
- •Conclusion.
- •Glossary of terms
- •Vocabulary
5.5 Border irrigation design
With two exceptions, the design of borders involves the same procedure as that for furrow systems. The first difference is that while the depletion and recession phases are generally neglected in furrow design, both phases must be included for borders. The second difference is that the downstream end of a border may be dyked to prevent runoff. One simplification of border analyses is that the geometry of the flow is simpler because it can be treated as wide, plane flow. The values of p1 and p2 are always 1.0 and 1.67, respectively.
5.5.1 Design of open-end border systems
The border designs given here assume the advance phase is completed before the inflow is terminated. Many irrigators, in fact nearly all where the downstream end is dyked, actually cut off the inflow before the end of the advance phase. In these cases, the volume of water on the surface will continue to advance along the border until it reaches the lower end where it will run off or pond in front of the dyke. Unless the border system is extremely well designed and operated, the downstream pond often creates a substantial threat to the crop in the submerged areas and although dyked at their lower ends, most farmers provide a surface drain for excess water. Consequently, the border efficiency and uniformity are approximately the same as borders in which excess surface water simply drains off the field after the advance phase is complete. The following procedure is therefore suggested for border systems where the excess surface water is drained from the field either by a completely open-ended border or by a regulated outlet from a blocked-end border.
5.5.2 Design of blocked-end borders
The computations needed to evaluate and design blocked-end borders where the flow is cut off before or shortly after the advance phase is complete are substantially more detailed than the procedures outlined above for furrow and open-end border irrigation systems. In fact, the volume balance methods given previously are relatively weak for this particular case of surface irrigation. Generally, the computations for blocked-end borders are best performed with zero-inertia or full hydrodynamic simulation models which are beyond the scope of this paper.
A number of studies have been made to develop relationships among the most important variables involving border irrigation using a dimensionless approach and the higher level simulation models. The interested reader might want to refer to Strelkoff and Katapodes , Strelkoff and Shatanawi , Shatanawi and Strelkoff , and Yitayew and Fangmeier for some of these reports.
The design procedure outlined below is an extension of the approaches already given and consistent with the level of treatment given herein. The procedure given here is intended to be conservative and will yield designs capable of performing at somewhat lower application efficiencies than is perhaps possible using the more comprehensive methods.
5.5.4 A blocked-end border design example
The problem. Section 8.5.4 illustrated the open-end border design procedure. The option of dyking these borders should be considered as an option for improving application efficiency. From results already available, the required intake opportunity times, rreq, needed to apply a depth of 8 cm (Zreq) were about 389 minutes and 679 minutes for initial and subsequent field conditions, respectively. Assuming the borders will run in the 200 m direction on the 0.1 percent slope as above, Figure 59 indicates the inflows that will complete the advance in the respective rreq times are 0.036 m3/min/m for initial irrigations and 0.0215 m3/min/m for later ones.
The values of r and p need to be generated or extrapolated for these flow rates unless they are already generated as part of the development of Figure 59 or, in this example case, from the previous example problem. For the 0.036 m3/min/m inflow, the values of r and p were determined from the previous example as r =.5635 and p = 6.949. For the 0.0215 m3/min/m inflow, r and p were calculated using the methods outlined in section 5.3.1 rather than extrapolated with the result that r =.6032 and p = 3.916.
