Sunday, September 22, 2019

Evaluation of MAR methods for semi-arid, cold region

Evaluation of MAR methods for semi-arid, cold region

Nasanbayar Narantsogt,
Karlsruhe University of Technology, Karlsruhe Germany
                                                                                 
Abstract:
The semi-arid and cold environment shows a high variability in precipitation and river discharge. The groundwater aquifer located near Ulaanbaatar capital city of Mongolia, is the only source of water supply and it is important to ensure that groundwater is available now and for the future.
The main watercourse near the city is the Tuul River, fed by precipitation in the nearby Khentii Mountains. However, due to the absence of precipitation during winter and spring, the riverbed usually runs dry during that time, and observations show that the dry period has been extending within the last years.
However, in parallel with the city’s development, the extended groundwater aquifer shows a clear decline, and the groundwater levels drop significantly. Therefore, a groundwater management system based on managed aquifer recharge is proposed and a strategy to implement these measures in the Tuul River valley is presented in this paper. It consists of an enhancement of natural recharge rates during the summer wet period, an increase of groundwater recharge through melting ice storage in dry period, as well as the construction of underground dams to accumulate groundwater also surface water reservoir which release constant discharge in outlet.  
The MATLAB icing code written for ice storage on limited and unlimited area was considered in FEFLOW simulation scenarios as water source in ice form on surface to increase groundwater natural recharge rates during the early dry period, through melting ice storages.  The study of underground artificial permafrost as ice dam was processed in FEFLOW simulation scenarios for accumulating groundwater resources. The results of these artificial recharging methods calculated individually and combined also compared with surface reservoir which release constant discharge through dam.


Keywords: Ulaanbaatar, drainage canal, icing, ice storage, underground dam, reservoir scenarios


1.      Introduction
The Tuul River flows through Mongolia’s capital city Ulaanbaatar (UB) which originates on highly Khentei mountains upper side of the city. The water level of the Tuul River fluctuates according to annual high-flow to low-flow cycles, with its average water flow being 26,6 m3/s. 4.
It also recharges the Ulaanbaatar aquifer that providing city’s water supply by 218 wells dividing 9 group of intake wells and 21 booster pump stations of water supply agency, daily domestic consumption fluctuates around 150-200m3/day depends on yearly season. See Figure-1. The company estimates that another 130.0 T.m3/day is pumped from the aquifer by private wells run by industries and individuals.
Figure 1: Groundwater aquifer south side of Ulaanbaatar city
a) Mongolian hydrological drainage basins; b) Tuul River through UB; c) UB water supply wells
The joint meeting of Mongolian and Russian mineral resources commission estimated the useful capacity of groundwater resources of Ulaanbaatar aquifer at 264.0 T.m3/day 21, without upper source lies upper city side from which explore around 24-48T.m3/day groundwater. 10
As with natural recharging formation of groundwater resources, the main balance components are water entering in the aquifer as a result of loss of surface runoff, and capacitive reserves of the upper water-bearing layer. During the period from May to December, the aquifer takes recharge due to the loss of the surface runoff at that time. In this period, replenishment infiltrates from the surface water to the stored groundwater capacitive reserves in the Ulaanbaatar aquifer.
In March and April, the groundwater table of water source aquifers decreases to a minimum of 8-10 m from the surface, but in June, July and August reaches a maximum level of 2-3 m under the earth surface in central source area.9 See Figure 2.
Figure 2. Groundwater table fluctuation depending on Tuul river flow [12]
Water demand increases daily with the development of city industries and ongoing population growth, but groundwater resource decreases due to the climate change and excess water usage. In the last decade, during spring (April and May), the dry period of the Tuul River flow continued longer than one month after ice breakup.
The following table shows calculated balance with outflow and inflow at the Tuul River valley aquifer, which is used for the water supply of Ulaanbaatar city. Tuul River discharge was taken as inflow rate, precipitation and evaporation amount averaged values over many years. Other inflow source tributaries to the Tuul River direct to aquifer for the water supply of Ulaanbaatar draining water from Selbe, Uliastai and Khul River obtained over the last ten years averaged discharge amount, but pumped water amounts from the sources for water supply city were taken from the year 2010. The balance calculation rate estimated by subtract total pumped groundwater from the sum of the inflows-river flows, precipitation and reuse water thermos power plants.
Qbalance=Qinflow-Qpumped+Qreused
Above estimated calculation is considered whole total water supply upper and city central sources of Ulaanbaatar aquifers with Tuul River annual average flow rate.
Table 1: Water exploration volume balance for water supply Ulaanbaatar city
Months
IV
V
VI
VII
VIII
IX
X
XI
XII
I
II
III
Total
Balance
 [M.m3]
10.95
79.72
125.38
216.15
231.68
135.96
42.82
5.81
-4.23
-5.74
-5.56
-4.76
828.18
sum [M.m3]
848.47
-20.29

The balance for a whole Ulaanbaatar aquifer including domestic and thermopower plants water consumption is shown above, sorted by hydrologic years from April where balance takes with positive value.
Total amount of water consumption Ulaanbaatar city used for water supply in dry, non-recharging season from Tuul river surface water, reaches about -20 M.m3 depending on from weather conditions and general precipitation in a given year. This water consumption is pumped from all 9 sources including upper source means balance between income as infiltrated from the Tuul river and outcome as abstraction rate by intake wells. 19. This means 20M.m3 explored without recharging from river.  The balance estimation between groundwater income and pumped water for domestic water supply from Ulaanbaatar aquifer source area without thermopower plants is -7.1M.m3 water.
Therefore, there is an urgent need to solve this problem through design of hydraulic structures for an underground dam, managed aquifer recharge and promotion of ice storage or build surface reservoir dam from which release constant controlled outlet water.
In the next chapter will be considered only for domestic consumption in the central source area of Ulaanbaatar aquifer. FEFLOW simulation was taken in the upper central source area A zone where only 23 wells for water supply. See Figure 3.   
2.      Materials and Methods
Over the last decade, every spring during the months March and April, Tuul River dried out or does not flow. Therefore, we need to address this problem by building a complex of hydraulic structures, establishing measures for flow control and building artificial groundwater recharge systems like drainage or flooding area near drink water extraction wells.
This study attempts to find suitable artificial groundwater recharging methods for the upper part of the central source groundwater aquifer, encompassing the water supply source area of the Tuul River valley inside Ulaanbaatar. The Central source of drinking water supply system established into operation 1959. Drinking water is extracted from 93 deep well pumps, with 7 booster pumping station. The capacity of source reserve is 114000 m3/day. Nowadays water extraction from 70-80 wells and its volume reach 87-90 T.m3/day supply to capital city. 10 figure-3.
Figure 3. Ulaanbaatar aquifer, central source area, simulated area
The central source A zone was simulated in FEFLOW simulation. The upper part of the central source intake area near well-68 takes recharge from river surface water until January where Tuul River flows under ice cover. After that period Tuul River freezes until riverbed bottom then groundwater decreases continue until May. But in western side of the A zone intake wells area near well-51 recharge comes not only from Tuul river it also recharges from the Uliastai River therefore recharge takes a place early in May. As shown in graph Uliastai River flow freezes early in November as a small river due to groundwater decrease begins from October and recharge begins May depends on melting water from both rivers.  See figure-4.
The groundwater recharging process runs as follows.
In the initial phase of the non existence of surface runoff  from end of April to early May, its groundwater level maximum decreases are observed. If their value is less than the flow of the river, then it becomes possible to streaming river downstream.
The icing phenomena is one of the most important parameters for semi-arid, highly continental climate condition and plays significant role in hydrological cycle and regime 1) in Mongolia. Icing or ice cover of rivers and lakes plays cold season for icing continues five to six Months and ice cover thicknesses reaches 0.8 to 3.2 meters. However, some mountains big rivers with more slope and bigger perturbation boulders in riffle section stayed open whole year do not completely freeze along the length.
A small river like Tuul frozen to the bed (2.5 Months) 21 and in the mid of April has not ice cover and some places is dry bed without flow. 
The average date of first ice occurrence on rivers is third week of October. The freezing of the rivers continues from the end of October lasts end of December. The ice cover duration averages 145 days. During the last 60 years, the annual mean air temperature in Mongolia has increased 1.660C with winter temperature increasing 3.610C, spring-autumn temperature 1.4-1.50C, and summer with no clear trend. Temperature has increased rapidly in the March, May, September and November and therefore the ice regimes of the Mongolian rivers has changed. 10
 Ice phenology has shifted by 3-30 days in terms of freeze-up and break-up dates and ice cover duration has shortened. Maximum ice thickness has also decreased from the 1960’s to 2000. 1.
Generally, for a surface ice cover to become firmly established, the mean (depth-averaged) temperature of water must be less than 20C, the daily average temperature must be less than -50C, and the wind speed must be less than 5m/s. 0.
The Uliastai River one of the tributaries Tuul river originates from Khentii mountains flows from north east side to south through Ulaanbaatar city contributes Tuul river in area where water supply wells of Central source for Ulaanbaatar city.
Icing - Aufeis accumulates during winter along streams and river valley in northern Mongolia where dominates semi-arid, highly continental regions environments. Here in Uliastai river build ice from mittle of October until end of December and melting process starting from end of March until end of April.
The icing dynamics depending on more from groundwater fluxes, that discharges alongside of main channel.  That side springs build ice sheets over frozen riverbed, where mainstream flows under ice cover. Here considered ice generating process and icing dynamics from middle of October to end of December 2017.
The main stream is flowing by main riverbed under ice cover but alongside spring stream is creating ice on the top of ice sheets. This phenomenon calls icing or Aufeis.  Icing – Aufeis are sheets of stratified ice formed by freezing consecutive water leaks. 7.
The water flows over existing ice layers. It forms by upwelling of by ground-water discharge or manmade drainage channels where groundwater discharge is blocked by ice, perturbing the steady-state condition and causing a small incremental rise in the local water table until discharge occurs along the bank and over the top of the previously formed ice.7
In the beginning of November where river flow freezing from side benches, spring discharge which have no longer extending energy frozen firstly.  After river bed completely freeze and takes ice cover then spring discharges leaks from under ice or ice hummock while is increased groundwater head and pressure flows over frozen ice sheets create next ice sheet. 
Groundwater flux coming on earth surface like springs create over ice top next ice sheet which fills lower ravines and smooths horizontal even ice sheet.
The groundwater flux alongside of the river drains through drainage canal built icing phenomena while springs flow bed blocked by ice and mainstream in main riverbed flows under ice cover.  In this section, Uliastai River is like gaining stream almost one of third of the flow discharges abstracts to the groundwater and groundwater come out side springs.
Thus, phenomena create side springs leakage from under frozen soil which flows over frozen soil and ice cover streams, fills ravines and lower lands, creates ice sheet on the ice until river valley would be even same horizon. After that, the average daily temperature is decreasing under -200C then groundwater leakage discharge decreases also head and pressure that means groundwater flux in underground flowing. Also, drained groundwater, spring charge from surface and groundwater decrease influences for quantity of groundwater amounts. The ice thickness measurements from 15-th and 30-th of December show that the thickness of Aufeis sheets not increased.
Such a way groundwater leakage like drained water or springs over frozen soil and ice cover create stratified ice sheets over ice sheets. Here in Uliastai river spring discharge 32 l/s small amount of water but it built ice thicknesses in some place until 1m thick.  Some of the rivers make ice sheets to several meters thick. The end of Aufeis built depends on discharge of Springs and quantity of Aufeis building river flow usually last decade days of December or first decade days of January where after longest December night begin colder days of the year. A bigger river such as Tuul is possible to create Aufeis until February. Aufeis typically melts out during summer until end of April sometimes beginning of May and will often form in the same place year after year. 7.
 From this icing ideas written MATLAB code and thus used for managed aquifer recharge for central source upper A zone accumulate ice storage due to use melt water for recharge in dry season.
This aufeis spreading dynamics over ice sheets extending size decreasing while decreasing air temperature day by day from -5 0C to -30 0C. The result shows that length of aufeis spreading is 2329m, widening 458m and 1.54m thick. The code for aufeis had simplified with same slope along flat area. The following code presents aufeis extending dynamics when spreading water courted with pipeline levees and from leakage point to courted pipeline levee 1500m. That’s mean length of ice storage is only 1500m. see figure 6. The result shows that length of aufeis spreading is 1500m, widening 400m and 2.72m thick, is thicker than unlimited area.
Figure 6: The water supply pipeline connecting wells to reservoir. 
The one of artificial recharging groundwater resources is the temporary and spatial redistribution of surface runoff, in beginning of winter to create ice formation. Figure 6. The surface runoff that flows over north side of the central section A zone through filtration channel, will be release water at the end of canal, thus create ice sheets over frozen sheet again.
There are three types of promoting ice creation ways in cold region in winter on the ground surface, in the underground open pit or channel and on the river bed. Two of them surface and underground ice creation were considered in FEFLOW simulation scenarios. See Figure 6.
The releasing water amount 1 m3/s beginning of November until middle of December create icing where days average temperature decreased under -5 OС.
From the following graph seen that northern drainage canal allow us to accumulate 1 m3/s flow water for a month from November to mid December 3.9 M.m3 water to store on surface. But with losses from evaporation and winter fog over frozen ice sheets also in melting season evaporation loss allowed only half of this quantity about 2 M.m3 to accumulate and recharge groundwater.
The melting water from Aufeis begins to flow and recharge groundwater early April where surface water flows only until central source area and flows underground.  Therefore, melt water from ice storage, recharge groundwater in central source A-A zone from north side from beginning of April until May where surface water flows until end of aquifer.
Ice accumulation from November to end of December also recharge groundwater while water flows through drainage canal. Then it is transferred to an artificial regime with the subsequent supply of water to the canals, functioning together until the period of ice formation, provided the ice accumulation from surface water on the end of canal.
Aufeis is an icing method bringing more recharging water in the middle of the study area for its other constituent subsections, and an ice wall increasing the backside of western boundary. The drainage canal filtrates through northern side and recharge occupies whole area from east to west boundary.
The all combination method includes an ice wall, icing and a drainage canal. The drainage canal filtrates water from east to west along the north side of the study area and rest released from it water as early winter creates icing. Thus, this icing method performs after drainage canal filtration ceases altogether.
As seen in the following Figure, recharge from the drainage canal begins in May and ends in November, with icing recharge beginning in the middle of March and lasting May, and the ice wall holding groundwater in backward from March until November.
In nature, we can reserve more water in ice form as Aufeis to help build some hydraulic structures such as a drainage canal or underground dam. Both these structures can help us to reserve water stores in underground as well as keeping them on the surface in ice form.
Using coldness and icing in a semi-arid, highly continental region such as Mongolia can increase groundwater resources. The nonconventional artificial recharging methods like discussed in this dissertation, such as ice storage, helps groundwater recharge in dry season, where there is no flow and dry beds in river systems.
From October to December surface water naturally accumulates and is kept in ice form from river flow in the semi-arid, highly continental region, of the study area. During the subsequent dry season, these sources increase and recharge potential water availability by melting water sources.
One possibility is to reserve water resources to regulate groundwater flux control in highly continental cold region to eleminate dry riverbeds and keeping primary source rivers, such as the Tuul, continuously flowing during low flow period by melting ice blocks.
 
Figure 7. The all variation combination in simulated area compare to measured groundwater level
In this calculation of FEFLOW simulation is taken the maximum differences between simulated in natural condition and simulation in each managed aquifer recharge scenarios. The result of FEFLOW simulation in each MAR methods scenarios demonstrates following results:
·         Single ice wall on western boundary alone in natural condition without drainage canal increases groundwater resources 516 T.m3/year.
·         The drainage canal through northern side filtrates groundwater around 1 M.m3/year
·         The icing on the end of drainage canal recharge groundwater resources in aquifer 1.6 M.m3 water
·         The aquifer additional recharge groundwater quantity of all combined MAR methods is 2.55 M.m3/year. [19]
4.      Discussion
A preliminary analysis, as presented in this study, was to identify low-cost MAR implementation measures adapted to the specific natural conditions of Northern Mongolia. Thus, coldness cold weather can use to keep water in ice form as well as a water resource in the winter season and be used during low flow dry season by melting ice where rivers have dried out.
The accumulated ice would be recharging groundwater in dry season from March to May by melting where is river bed dry no water any cover ice there.
To find total additional water resource recharged by Northern drainage canal and Ice storage should increase abstraction rate until maximum possible rate when GW drawdown decrease under bottom of wells filter screen, soaks up air.  For a calculation of potential maximum abstraction quantity without MAR methods in the central source A-A zone, should estimate FEFLOW simulation until in some well groundwater drawdown reaches bottom of the well screen pump air instead water.  Such a way can establish groundwater fluctuation ranges in FEFLOW.
The groundwater fluctuation graph of monitoring well N8 show that, by increasing daily extraction to 60986 m3/day is could not pump water while groundwater drawdown is under bottom screen.  But in the middle of group of wells where happens extreme drawdown of groundwater level there only 45121 m3/day is possible. Therefore, maximum abstraction rate of this area is 45121 m3/day, which means 16469165 m3/year=16.5 M.m3 water per year.
Nowadays the exploitation rate is (average of 2009-2011) 20329 m3/day, 7.5 M.m3/year half of possible maximum abstraction.
The recharge quantity with MAR method then maximum abstraction rate increases until 70133 m3/day means 25.6 M.m3/year.
Difference between above maximum abstraction simulations show that groundwater resource possible to increase after MAR methods over extraction rate around 25 T.m3/day. That means approximately 912500 m3/year=9.125 M.m3 could additional groundwater during wet season could keep as reserve in this central source area upper part A-A zone.
The percentage of each MAR methods for a recharge groundwater resources in this area estimate so that sum of total amount of all methods is taken 100% from it respectively percentages for each method.
The percent of increased amount of water reserve by each method in combination of MAR methods increased groundwater sources is following.
·         drainage canal brings 73.5 % of artificial recharging 6.7 M.m3 water (1 m3/s discharge water through drainage canal from May to November 86400m3/day * 184day=15897600m3=15.9M.m3).
·         Ice storage keeps water in ice form 21% mean 1.9 M.m3 (1 m3/s discharge water for ice storage would be 5.2 M.m3 but fog and evaporation by icing and melting brings huge loss)
·         Ice wall, which delays groundwater flux, and keep groundwater table stable leads to keep 5,65% of increased groundwater. It is about 516 T.m3 water amount [19].
All these FEFLOW simulations were simulated in transient model where river surface water level increases wet season over river bed and dry season decrease under river dry bed. The eastern and western boundary groundwater table fluctuates under surface depends on recharge from river yearly.
Another different simulation scenario is for surface water reservoir with dam from which release water with constant quantity 26.6m3/s rate and create constant groundwater water table. In this case taken steady model with eastern and western boundary with constant groundwater level and hydraulic head also southern boundary as Tuul river with constant level value to recharge groundwater. The FEFLOW simulation for maximum abstraction rate reached here 90288м3/day. After that the simulation demonstrates error report that the aquifer has no groundwater. Figure 8.
Figure 8. The groundwater contours and error by pumped groundwater 166700м3/day
This means the flow control by surface reservoir accumulates flood water and additionally recharge groundwater quantity for central source A zone is 16.5 mio.m3/year.
The flow control upper reservoir release constant outflow whole year that means it also recharge central source B zone, occupying double sized bigger area with 50 intake wells. The whole central source area recharge from reservoir releasing constant rate would be 49.5 mio.m3/year. Also accumulated water in reservoir about 350 mio.m3 would be reserved fresh water resource. All these simulated calculations were recharging water only from reservoir.
When we are simulating combination of an artificial recharging groundwater sources and reservoir releasing surface water recharge than additional recharged groundwater would be 167700 m3/day. See figure 10.  
Figure 9. The groundwater simulated contours by combination managed aquifer methods and recharge from Tuul river outflowing from reservoir.
Figure 9. The groundwater simulated contours by combination managed aquifer methods and recharge from Tuul river outflowing from reservoir.
This MAR methods and reservoir recharge system include following simulation scenarios
·         northern drainage canal recharge groundwater resource from northern side in wet season
·         ice storage recharge groundwater by melting ice in dry season
·         until permafrost 5-10 m [5-6] underground ice dam which accumulates groundwater backside
·         surface reservoir with constant release discharge in Tuul river which recharge this area from southern side whole year
In this combination scenario possible maximum abstraction rate is increased to 167700 m3/day after that simulation. The maximum possible abstraction quantity for year reaches 44,7 mio.m3/year.
Here FEFLOW simulation run only for central source A zone when we take second B zone with 50 wells this maximum abstraction rate would be increase at least double 89,5 mio.m3/year because B zone two times bigger as A zone. If Tuul river flows yearly with constant discharge, then river surface water will be recharge for industrial source and that increase additional groundwater resource. This will be increase groundwater sources 149 mio.m3/year and create natural condition for Tuul river discontinuously flow that help avoid risk of fresh water supply shortage for Ulaanbaatar city.   
5.      Conclusions
The managed aquifer recharging methods taken in this simulation variants are northern drainage canal which recharge groundwater from opposite side as Tuul river, icing or Aufeis keeps water in ice form brings it from end of wet season through winter to the dry season, increase groundwater sources by melting, in the end of upper part of aquifer western side build underground dam which accumulate groundwater backside. All these variants are in FEFLOW simulated and the recharged quantity were calculated separately and combined are demonstrated following results.
·         Single ice wall on western boundary alone in natural condition without drainage canal increases groundwater resources by 516 thousand.m3/year.
·         The drainage canal through northern side filtrates groundwater around 1 mio.m3/year
·         The icing on the end of drainage canal recharge groundwater resources in aquifer 1.6 million.m3 water
·         The aquifer additional recharge groundwater quantity of all combined MAR methods is 2.55 million.m3/year. [19]
The additional recharged groundwater difference by increased daily abstraction rate from this aquifer with and without managed aquifer recharge would be 9.16 mio.m3/year.
When in FEFLOW simulation scenario has taken surface water reservoir which release constant discharge flow then recharge from only reservoir separately and combined simulation with MAR methods calculations demonstrated following results.   
·         The recharge quantity from the Tuul river with constant discharge entire year 16,5 million3/year.
·         The combination MAR and surface water from reservoir outflow recharges 44,7 million.m3/year.
These simulation results only from upper part with 23 wells of central source area which has total 72 wells. When simulate whole Ulaanbaatar aquifer then additional recharged groundwater resource from Tuul river flow with constant runoff would be at least 3 times more than this small area as 150million.m3/year.
The simulation both transient (MAR methods) and steady reservoir outflow recharge methods show that groundwater artificial recharge methods not enough for additional recharged quantity compared to surface reservoir outflow recharging. But combination of both methods demonstrates more effective for an artificial recharging groundwater sources in aquifer.
The Tuul river reservoir will be locate upper from aquifer, would be accumulates 350 million.m3 creates more humidity environment in Ulaanbaatar region. A positive side effect of increased evaporation from the open water is that air humidity will be increased which will lead to artificial precipitation and a deposition of atmospheric particles from air pollution and thus help to improve air quality in the city and its surroundings.
Groundwater flux disturbed by the presence of an ice wall come out on surface during spring, spreading, evaporating and losing some quantity. This makes a fog in winter season and originates turbidity in air where cold high-pressure cyclone dominates in Ulaanbaatar city. Turbidity of air makes windy surroundings and clear air pollution.
This MAR method water storing in ice form in semi-arid, cold highly continental region, would be also produce coldness 2 during dry season and increase the inner continental hydrologic cycle by melting and evaporating. In dry season ice melt evaporates and increases precipitation. Every year in dry season many forest fires occur in Mongolia, at least partially due to no precipitation and lower air humidity. Therefore, ice-keeping methods would help us to keep the environment green, environmentally close to natural process to improve human and natural habitats.
The Aufeis blocks, icing made in river valley is increasing inner continental cycle by evaporating meltwater. Thus, it helps to grow up vegetation and increase precipitation in dry period.  During fall months, from September October, with more rain soil moisture increases and during spring (March April) there is more humidity in the air and more rain. (by personal observation.) Meltwater is the mean source for rivers continuously flowing and recharging groundwater aquifers. Around the icing area, natural grown bushes and trees as well as designed recreation areas could renature the environment for the local population.
References
1.        Ashton, G. D., Deterioration of floating ice covers, J. Energy Resour. 177-182, 1985
2.        Batima Punsalmaa, Batnasan Nyamsuren, Bolormaa Buyndalai (2004). Trends in River and Lake Ice in Mongolia.  AIACC Working Paper No. 4
3.        Davaa Gombo, Erdenetuya Magsar. Hydrological Changes in the upper Tuul River Basin (2004). Institute of Meteorology and Hydrology, Juuljinii St. 5, Ulaanbaatar-46, MONGOLIA
10.     GIM - Geoecology Institute of Mongolia (2000): The current situation, location, reserves and future concept of domestic and industrial water supply for Ulaanbaatar city.
11.     George D. Ashton Thin ice Growth WATER RESOURCES RESEARCH,VOL. 25, No 3, Pages 564-566, March 1989
13.     Kresic N (2006) Hydrogeology and groundwater modeling. CRC press, S. 807
14.     Kimrey. J.O, Artificial recharge of groundwater and its role in water management
15.     Kuroda, T., Rate determining processes of sea ice growth, Ann. Glaciol., 6, 168-170, 1985.
16.     L. Emerton, N. Erdenesaikhan, B. de Veen, D. Tsogoo, L. Janchivdorj, P. Suvd, B. Enkhtsetseg, G. Gandolgor, Ch. Dorjsuren, D. Sainbayar and A. (2010) The Economic Value of the Upper Tuul Ecosystem, Mongolia
17.     Maki Tsujimura, Koichi Ikeda, Tadashi Tanaka, Lunten Janchivdorj, Badamgarav Erdenchimeg, Damdinbazar Unurjargal, Ramasamy Jayakumar  (2013): Groundwater and surface water interactions in an alluvial plain, Tuul River Basin, Ulaanbaatar, Mongolia. Sciences in Cold and Arid Regions, 126-132
18.     Mongolian climate and surface water reserve atlas (1985) Ulaanbaatar.
19.     N.Nasanbayar, N.Goldscheider, S.Chuluunkhuyag (2018). Icing for MAR methods for semi-arid, highly continental region. Conference paper. Harbin. China. iFOST 2018
20.     SIWRMM “Strengthening Integrated Water Resources Management in Mongolia” project. Tuul River basin integrated water resources management assessment report. (2012).
21.     RIBES-Research Institute on Building Engineering Studies. (1979): Technical report of engineering survey TOM-2 . Moskow
22.     Reddy, K. R., (2008). Enhanced Aquifer Recharge: Overexploitation and Contamination of Shared Groundwater Resources Springer Netherlands.
23.     Robin Grayson. (2010) Asian Ice Shields and Climate Change World Placer Journal-2010. Volume 10, pages 21-45.

No comments:

Post a Comment