Qanat is an ancient water harvesting technology which is used for irrigation, agriculture and drinking in many countries of the world. A key element of preserving this heritage is calculating their protection area. In this study, the main aim is depiction of the hydraulic harim of qanat with the usage of the meshless numerical method. Afterward, the qanat package has been added to this model to delineate the hydraulic harim of the qanat. Two qanat systems are shown here: one in a standard aquifer and the other in a real test case, namely Haji-Abad qanat, located in the Birjand unconfined aquifer. In the real test case, the hydraulic harim of Haji-Abad qanat with 10 collection shafts is depicted in 3 time sections as well. The time sections are 3 years after extraction (2014), 6 years (2017) and 11 years (2022). The findings stated that time makes the harim area larger. In addition, the hydraulic harim is extended to areas with a higher hydraulic conductivity coefficient. Ultimately, we have delineated the hydraulic harim for 2040 and unfortunately, it is influenced by buildings. Therefore, it is necessary to find the hydraulic harim of qanats in order to protect this traditional heritage.

  • This method is applicable for all qanats with different conditions.

Today, due to Iran's annual rainfall of 250 mm yearly, equivalent to one-third of the world average, groundwater resources are becoming increasingly critical (Jafarzadeh et al. 2022). It has created many issues regarding the provision of water for agriculture, drinking and other uses. One of the oldest and most efficient methods of harvesting these resources is the use of qanat or kariz systems (Al-Ghafri et al. 2003), especially in semi-arid and arid areas (Samani et al. 2022). Although modern methods have surpassed them, the qanats still play a major role in the continuity of settlements, even today. This is why they have been used for more than 2,500 years, especially in Iran (Maghrebi et al. 2022).

These systems are naturally and socially sustainable (Khaneiki 2022). Sadly, they have been threatened for the past decades and faced unprecedented challenges for various reasons, including aggressive groundwater pumping which reduces qanat flow rates and its productivity, increased development and urbanization (Esmaeili et al. 2022). Another important reason is the excavation of a new qanat on the hydraulic harim of the other qanats which threatens the older qanat with drought (Salek 2019). Therefore, the qanat systems are under a significant threat of dying out. However, they are vital to water management in Iran (Khosravi et al. 2016).

A key legal concept relating to the qanat system is the law of harim, or borders, which protects the owner of a qanat over a territory surrounding it and prohibits the construction of new mother wells or any other structures within a defined distance of existing qanats (Albert et al. 1998; Hein 2020). On the other hand, harim, a protected area around each well that prevents new wells from affecting the yield of existing wells, is defined for tube wells as well as qanat mother wells, but the harim for qanat mother wells is much broader than that for tube wells (Lightfoot 1996).

The harim law does not specify this distance. In Al-Karaji's discussion, it is apparent that distance depends on the type of hydro-infrastructure, type of qanat, its length and depth, geological condition of the soil, location of the mother well, etc. (Albert et al. 1998). So, harim is more than just protecting ownership rights; it also defines the framework for protecting groundwater resources.

Technically, harim qanat (quantity capture zone) refers to an imaginary line that connects the shafts of the wells at a certain distance from its sides (the axis of the qanat's tunnel). The distance between the axis of the qanat's tunnel and the point at which the qanat's drainage effect on the groundwater level is negligible and can be ignored (Mousavi & Sarhadi 2019). Its amount varies in different qanats and depends on several factors, including the hydrodynamic characteristics of the aquifer in which the qanat is dug. The harim of a qanat increases as it gets closer to the mother of the well (Ministry of Energy 2015). Harim of qanats is proportional to the extent of their exploitation in terms of their purpose. As an example, a harim qanat whose average flow rate is 200 L/s is more than a harim qanat whose average flow rate is 50 L/s. Figure 1 shows the schematic cross-section of Harim in a qanat.
Figure 1

Cross-section of qanat.

Figure 1

Cross-section of qanat.

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As a result of not paying attention to such critical issues in the last few decades, Iran has encountered a number of serious problems. According to Khosravi et al. (2016), the urbanization of the northern areas of Tehran after the 1960s disrupted the practice and application of harim to older qanats: the deep foundations of many buildings blocked underground water flow.

The importance of harim in qanats has been stressed in many studies over the years. Lightfoot (1996), in order to speak about the shaft and well's placement alongside each other, presented the concept of hydraulic harim and expressed that this area for the mother well is larger than other shafts (Lightfoot 1996). Balali et al. (2009) indicated the effects of modernization and urbanization problems on qanats. Therefore, they expressed the concept of harim and noted that it is usually within 100 and 300 m (Balali et al. 2009). Wessels (2011) brought the regulation about the hydraulic harim and stated the laws about it in order to avoid problems for qanats (Wessels 2011). Aroua (2014) presented the concept of ‘harim-al-ma’ and its importance in order to reduce the health problems of water exploited from qanats. The case study was M'Zab Valley, including four cities covering an area of 300 km2 (Aroua 2014). Nabavi (2017) spoke about the harim law. The first benefit of the law is that it preserves established water rights across the country through a concept called ‘harim’ and, a new qanat or well cannot be excavated in that area (Nabavi 2017). Salek (2019), after an explanation of the harim concept, mentioned the necessity of harim determination and stated that this area usually started from wells and shafts and continued until 1.2 km from them (Salek 2019). Mirnezami et al. (2019) presented the definition of harim as the protection zone of qanats and wells according to ancient Islamic tradition (Mirnezami et al. 2019).

Hein (2020) illustrated the parameters affecting the harim of qanats and discussed the challenges that come from building something in the harim area (Hein 2020). Gharios (2020) wrote about harim, its definition and its aim for all water resources (Gharios 2020).

Simonen (2021) indicated that harim is another important aspect of qanats which directly affects inter-communal and intra-disputes (Simonen 2021). Mohan & Kuipally (2021) explained the harim rule for some water resources like wells and springs and stated that this rule identifies the minimum distance between two water point sources (Mohan & Kuipally 2021).

Studies in which the harim of the qanats are drawn are rare, and all of them use empirical formulas with ArcGIS software. Mathematical equations like Sichardt and drainage channels are used for this aim. Mousavi & Sarhadi (2019) determined the hydraulic harim with the usage of ArcGIS software. They overlaid some layers on each other to export the final raster. The raster is achieved by the Sichardt equation presented in Equation (1) and as it is obvious, harim radius () is dependent on drawdown () and hydraulic conductivity coefficient () (Kyrieleis & Sichardt 1930).
(1)

It was reported that the length of Dash-Bolagh qanat in Hamadan plain – an Iranian plain – is around 1,150 m. They also stated that Ali-Khan-Kahrizi qanat has the least length of 13 m. Mirzaei Yazdi et al. (2020) used FEFLOW software in order to simulate groundwater flow. Then with the help of ArcGIS, delineated the hydraulic harim for a standard aquifer. The Sichardt equation was used for the computation of hydraulic harim on that aquifer (Mirzaei Yazdi et al. 2020).

Previously, the qanat's harim area was mainly determined using these formulas, but there were never any standard, user-friendly and more accurate methods for determining this area. Currently, there is an urgent need to find a model that is compatible with all complex conditions of aquifers, has the flexibility to consider different hydrodynamic coefficients near the qanat system, has the ability to take into account the passage of time and is close to real conditions. For this reason, numerical models based on groundwater flow equations were investigated in order to be able to determine the harim of these resources in a more accurate and faster manner to achieve more realistic results.

In this regard, some numerical methods can be used for this aim. Finite difference, and finite element are the traditional numerical methods (Wang & Anderson 1995). Due to their dependency on the meshing stage, some errors exist in their results. However, a new group of numerical methods named the meshless method, presented in the last decade which removes this drawback and releases results with higher accuracy than the traditional methods (Liu & Gu 2005). Meshless local Petrov–Galerkin (MLPG) is one of the numerical methods which can be used for fluid dynamics for this aim (Atluri & Zhu 1998). Mohtashami et al. (2017, 2021) developed MLPG for groundwater simulation in both steady and unsteady states. They found their model more accurate than the finite difference method (Mohtashami et al. 2017, 2022a).

Delineation of hydraulic harim using the numerical method is not investigated in the previous studies. In this study, the hydraulic harim of a qanat system is depicted using the MLPG numerical method. This was done for the first time during this research; after introducing the qanat system to the developed model, the hydraulic harim will be delineated for the collection section. This developed model is applied to two standard and real field study aquifers.

Qanat system

Figure 2 illustrates the structure of a qanat system in an unconfined aquifer. The aquifer in the study area is saturated. The first well is the mother well, which has the maximum flow rate. Other wells are located in both the collection and conveyance sections.

During the generation of the cone of depression, the shaft in the collection section has a hydraulic harim. Our purpose in this study is to define this area.

A user should protect the qanat and its domain (harim) from pollution and any source of poisoning. In areas with hard soil, Harim is usually bounded by 1.2 km, and in areas with soft soil, by 0.5 km (Salek 2019). As a result of the right/duty of domain protection, the water users of the qanat could reach the shafts in case of any maintenance and protect the qanats from activities that could negatively affect the purity of the water or the functioning of the qanats along the wells.
Figure 2

Cross-section of a general qanat system (Samani et al. 2022).

Figure 2

Cross-section of a general qanat system (Samani et al. 2022).

Close modal

Case studies

Standard aquifer

Sharief et al. (2008) studied a confined aquifer illustrated in Figure 3. This structure has an area of 1,800 × 1,000 m2, a thickness of 10 m and a storage coefficient of 0.0004. The aquifer in two regions is recharged at a rate of 0.00024 and 0.00012 m/day (Sharief et al. 2008). Three extraction wells are also found at (800,200), (800,800) and (1,400, 600). In these wells, 200, 500 and 700 m3/day of water are extracted. The injection well is positioned at (400,800) coordinates and recharges the aquifer at a rate of 800 m3/day. There are three zones in the aquifer. A different transmissivity coefficient is present in each zone along the x and y axes. Figure 3 shows the boundary conditions for both the west and east edges. The north and south sides are also impervious. Three observation wells are located at (600, 400), (1,600,400) and (1,000, 600) and are depicted in blue color.
Figure 3

Standard aquifer representation. Please refer to the online version of this paper to see this figure in colour: http://dx.doi.org/10.2166/hydro.2023.020.

Figure 3

Standard aquifer representation. Please refer to the online version of this paper to see this figure in colour: http://dx.doi.org/10.2166/hydro.2023.020.

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Real aquifer

The Birjand plain, located between 58°41′E and 59°45′E longitude and 32°34′N and 33°7′N latitude, is one of the main areas under study in the Lut Desert. Figure 4 shows the basin in Iran and its elevation. The area has an almost rectangular shape with an average length of 131 km and an average width of 26 km. Its perimeter is 313.8 km, and its area is more than 3,400 km2.
Figure 4

Birjand unconfined aquifer and its geographical location.

Figure 4

Birjand unconfined aquifer and its geographical location.

Close modal

Between 1955 and 2021, the average yearly rainfall was 145.9 mm. The average amount of rainfall in the plains was estimated at 166.3 and 173.4 mm/year in the mountainous area. Based on regional classifications, this area is categorized as arid, and its average yearly temperature is 16.6 °C. The amount of summation of evaporation in the heights of the area is calculated to be 2,234.26 and 4,607.19 mm in the plains.

Meshless local Petrov–Galerkin

MLPG is one of the weak-form meshless methods that enforce governing equations in nodes instead of elements. In 1998, Atluri and Zhu introduced it for the first time to solve the potential equation. Their emphasis was on the effectiveness and accuracy of this method in solving equations, especially those relating to fluid mechanics. MLPG enforces the governing equation on each node and then assembles the equations in one matrix in order to find the unknown coefficient (Atluri & Zhu 1998).

This method for groundwater flow simulation in the Birjand aquifer was first developed by Mohtashami et al. (2017). They calibrated and validated their model and found their model to be more accurate than traditional methods.

Governing equation

Confined aquifer

The groundwater equation in unsteady state for the confined type of aquifer is illustrated in the following equation (Wang & Anderson 1995; Todd & Mays 2004):
(2)

Here, H is groundwater head, k denotes hydraulic conductivity coefficient, Q shows the discharge (+) or recharge (–) rate, S is the storage coefficient and q indicates the precipitation and evaporation.

After the discretization of the groundwater flow equation, a set of linear equations is generated in the form of as explained by the following equations (Mohtashami et al. 2021):
(3)
(4)
(5)

In Equation (3), W and represent weight and shape functions. Here, K, F and U represent the stiffness matrix, force body vector and the unknown variables vector.

Unconfined aquifer

The governing groundwater equation in an unconfined aquifer according to Todd 2005 is presented as the following equation (Todd & Mays 2004):
(6)
and are hydrodynamic parameters, hydraulic conductivity coefficient and specific yield, respectively. H is the groundwater table and Q is the flow rate of wells, qanats. q shows the precipitation and evaporation values. The equation considering the following substitution can be written again (Mohtashami et al. 2017):
(7)
(8)
As the aquifer is homogeneous and isotropic (.):
(9)
After some discretization rm of equations is generated . This set is easily solved by Gauss Jordan algorithms (Mohtashami et al. 2017).
(10)
(11)
(12)
is the weight value of i-th node, is the shape function, is the time step (1 month), is the domain (aquifer). K, U and F are the stiffness, unknown and force body matrix, respectively (Mohtashami et al. 2022b).

Model development

Steps for delineating hydraulic harim are presented in the following figure.

In Figure 5, two packages exist. The first package is the MLPG simulation model which accumulates all the input data, such as hydraulic conductivity coefficient, specific yield, extraction or injection flow rates and so on. Then the qanat package entered into the MLPG in order to define the detail of the qanat system in the simulation model.
Figure 5

Flowchart of the presented study for hydraulic harim depiction.

Figure 5

Flowchart of the presented study for hydraulic harim depiction.

Close modal

Details like the location of a mother well, shafts and the gallery are entered into the model; also, with the usage of the Darcy equation, the flow rate of a mother well and shafts are calculated and assigned to the model. After all, the groundwater head is computed. With the initial groundwater head, the drawdown value presented by ‘s’ is computed.

At the final stage, the nodes placed in the area with the determined drawdown are illustrated. Based on the drawdown values of these nodes, contour lines will be drawn and hydraulic harim will be depicted in the aquifer.

The MLPG numerical method is going to be used to delineate hydraulic harim within the collection section of qanats. In this way, the drawdown value for the aquifer which is caused by the extraction of qanats is computed and based on that, an area for different drawdowns is plotted.

In order to find the drawdown values, the groundwater equation must be solved. To this end, MLPG is used. Solving an equation with MLPG has three steps: pre-processing, processing and post-processing. In the pre-processing stage, in the aquifer and its boundary, defined numbers of nodes are uniformly distributed. Each node has five layers of information containing: hydraulic conductivity coefficient, specific yield, initial groundwater head, boundary condition and recharge or discharge value (Mohtashami et al. 2017). After these layers are assigned, the processing stage begins, and the stiffness and force body matrices are calculated. During the last stage, groundwater head and after that drawdown values are computed and contour lines are drawn. According to these lines, this area can be achieved.

It is noteworthy to state that MLPG was a calibrated and verified model for groundwater flow simulation based on previous articles by the authors. This model in both unconfined and confined conditions, steady and unsteady forms, was calibrated and validated and applied to standard and real aquifers. Results are achieved by Mohtashami et al. (2017, 2021). In these studies, groundwater head which is presented by MLPG was compared to MODFLOW results (which is based on the finite difference method) and other meshless methods. MLPG had higher accuracy than other numerical methods. This was shown with three evaluation indices. Root mean square error (RMSE), mean absolute error (MAE) and mean error (ME) were these indices. Table 1 shows the performance of MLPG for standard aquifer and Table 2 is for Birjand unconfined aquifer as a real test case according to the mentioned evaluation indices.

Table 1

ME, MAE and RMSE for standard aquifer (Mohtashami et al. 2021)

MLPG (m)Point collocation polynomial method (m)
ME 0.0716 0.0021 
MAE 0.0716 0.0021 
RMSE 0.006 0.191 
MLPG (m)Point collocation polynomial method (m)
ME 0.0716 0.0021 
MAE 0.0716 0.0021 
RMSE 0.006 0.191 
Table 2

ME, MAE and RMSE for Birjand unconfined aquifer (Mohtashami et al. 2017)

MLPG (m)Finite difference (MODFLOW) (m)
ME –0.08 0.159 
MAE 0.573 1.434 
RMSE 0.757 1.197 
MLPG (m)Finite difference (MODFLOW) (m)
ME –0.08 0.159 
MAE 0.573 1.434 
RMSE 0.757 1.197 
Table 3

Specification of mother wells and collection shafts

X (m)Y (m)Flowrate (m3/day)
Mother well 500 500 156 
Shaft #1 600 500 109 
Shaft #2 700 500 62 
Shaft #3 800 500 15 
X (m)Y (m)Flowrate (m3/day)
Mother well 500 500 156 
Shaft #1 600 500 109 
Shaft #2 700 500 62 
Shaft #3 800 500 15 

Harim in standard aquifer

In order to draw the hydraulic harim of a qanat system, we first move through the standard aquifer and consider that the standard aquifer has one qanat system and is unconfined. This system includes one mother well, three shafts in the collection section and three shafts in the conveyance part. The volume of water drained from the mother well and shafts placed in the collection section is computed with the Darcy formula. In this way, Table 3 details the location and flow rate of the mother well and collection shafts. There is no drained flow rate in shafts placed in the conveyance section because the groundwater table is at a lower depth than these shafts.

Figure 6 shows 777 points scattered on the boundary and inside the aquifer (112 on the boundary and 665 inside). The arrangement of nodes in the aquifer is illustrated in Figure 6. The distance from each point to an adjacent point is equal to 50 m.
Figure 6

Arrangement of nodes in standard aquifer.

Figure 6

Arrangement of nodes in standard aquifer.

Close modal

Simulations were conducted and a model was run for this standard aquifer. Hydraulic harim was depicted for three time sections, 30, 60 and 120 days after exploitation from the qanat.

Hydraulic harim for the collection section of qanat is depicted. The area was drawn for 30 days of extraction from qanat. In the collection section, the mother well and two shafts have remarkably large areas of harim, but at the third shaft, no harim is visible.

Figure 7 demonstrates that most drawdowns occur in wells (mother well and two shafts), and this is evident from the yellow hue of the harim. The area of the hydraulic harim is 25,000 m2 and its width and length are 100 and 200 m, respectively.
Figure 7

Hydraulic harim depiction for standard aquifer in 30 days.

Figure 7

Hydraulic harim depiction for standard aquifer in 30 days.

Close modal

It should be noted that the drawdown values for the mother well and the two shafts are 4.5, 4.1 and 4 m, respectively. We delineated this area after 30 days extraction from qanat.

According to this figure, there is no hydraulic harim for the third shaft. This is because of the short time of extraction and the low level of water table on the node.

The following figure presents the hydraulic harim for 60 days extraction.

The hydraulic harim of the qanat system on 60 days after extraction is shown in Figure 8; the width of the harim is wider than in Figure 1, indicating that more water had been extracted from the aquifer. In this condition, the third shaft has not shown drawdown yet, and the reason is the low water table in this shaft.
Figure 8

Hydraulic harim depiction for standard aquifer in 60 days.

Figure 8

Hydraulic harim depiction for standard aquifer in 60 days.

Close modal

The area of the harim is 42,500 m2, the width and length are 200 and 400 m, respectively. Both of these values have increased over the previous figure.

Figure 9 shows hydraulic harim after 120 days of exploitation.

You can see that in this case, harim is created around the third shaft, but it is too small in comparison to the others. This is the final harim, because after 109 days, the aquifer reaches its steady state and the cone of depression does not change. Therefore, this area remains constant after 109 days, even after 120 days.

This harim has the most area, length and width values in this situation, also the mother well and the three shafts have the greatest drawdown value. However as mentioned previously, the drawdown after 109 days remains constant.

As a result, Table 4 shows the area, width and length of hydraulic harim for standard aquifers in different time sections.

Table 4

Hydraulic harim specifications

Time section (day)Area (m2)Length (m)Width (m)Max drawdown (m)
30 25,000 200 100 4.5 
60 42,500 400 200 4.7 
120 50,000 400 200 4.8 
Time section (day)Area (m2)Length (m)Width (m)Max drawdown (m)
30 25,000 200 100 4.5 
60 42,500 400 200 4.7 
120 50,000 400 200 4.8 
Table 5

Drawdown values at mother wells and collection shafts

0 Days30 Days60 Days120 Days
Mother well 4.5 4.7 4.8 
Shaft #1 4.1 4.3 4.5 
Shaft #2 4.05 4.2 
Shaft #3 3.7 3.9 
0 Days30 Days60 Days120 Days
Mother well 4.5 4.7 4.8 
Shaft #1 4.1 4.3 4.5 
Shaft #2 4.05 4.2 
Shaft #3 3.7 3.9 

As a result of Table 4 and 5 there are some points. The length and width of the hydraulic harim for the two time sections (t = 60 and T = 120 days) are equal; however, their area is different. This is because the hydraulic harim is almost fully formed except for the third shaft. The third shaft took its own formation after 109 days of exploitation. As time passed, this value grew, and in different sections of time, the max value was associated with the mother well. Notice that the drawdown would not be changed after 109 days. This is due to the conversion of an unsteady state to a steady state after a period of exploitation (Figure 10).
Figure 9

Hydraulic harim depiction for standard aquifer in 120 days.

Figure 9

Hydraulic harim depiction for standard aquifer in 120 days.

Close modal
Figure 10

Hydraulic harims for different time sections.

Figure 10

Hydraulic harims for different time sections.

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Harim in real test case

The Birjand unconfined aquifer has 15 qanat systems. The outlet points of these qanats are displayed in Figure 11. One of the most famous qanats in Birjand, named Haji-Abad, was chosen for hydraulic harim depiction aims. Haji-Abad qanat is one of the longest qanats in this aquifer with a 2,500 m length. Its flow rate also in comparison to other qanats is higher. The number of shafts is numerous. Both collection shafts and conveyance shafts exist in this qanat. However other qanats in this aquifer have low flowrate and no collection shafts. In this way, the best choice is Haji-Abad qanat.
Figure 11

Haji-Abad qanat location and outlet. Please refer to the online version of this paper to see this figure in colour: http://dx.doi.org/10.2166/hydro.2023.020.

Figure 11

Haji-Abad qanat location and outlet. Please refer to the online version of this paper to see this figure in colour: http://dx.doi.org/10.2166/hydro.2023.020.

Close modal

The length of this qanat is 2,500 m. Its flow rate range is [15–45] L/s, the depth of the mother well is 75 m and the number of shafts is 150. Water extracted from this qanat is used for agricultural irrigation. The path of this qanat is depicted in Figure 11.

Figure 11 shows the nodes scattered uniformly around the qanat outlet, as well as its path, tunnel and mother well. In order to draw the hydraulic harim of Haji-Abad qanat, first, the conceptual model for the Birjand aquifer was created. Then, the qanat package was entered into the MLPG simulation model. The location of the mother well, collection shafts and outlet were defined in the meshless method and is assigned to the nearest node. They are represented in blue, green and red symbols in Figure 11. The waterway of qanat is also shown in the same figure with a blue line. It is noticeable that the flow is heading toward the west. Figure 11 also shows the outlet of Haji-Abad qanat.

Simulation of groundwater flow was done for 11 years with a monthly time step (2011–2022). Then, the hydraulic harim for the chosen qanat in different time steps was computed and depicted. The simulation was run under the assumption that exploitation started in 2011 and would continue until 2022. Time steps were 3, 6 and 11 years.

Hydraulic harims have different area values as time passes. In Figure 12, yellow nodes indicate nodes that are located in the hydraulic harim of Haji-Abad qanat.
Figure 12

Hydraulic harims for Haji-Abad qanat in three time sections. (a) 2014, (b) 2017, (c) 2022.

Figure 12

Hydraulic harims for Haji-Abad qanat in three time sections. (a) 2014, (b) 2017, (c) 2022.

Close modal

Some points are derived from Figure 12: 1 – hydraulic harim area gets larger due to time passing. In other words, the number of yellow nodes is higher for harim of 11 years than 6 years, and for harim of 6 years than 3 years. 2 – hydraulic harim near the mother well is more extended than the other collection shafts. This is due to the higher groundwater table around the mother well which causes more flow rate than others.

3 – Extension of hydraulic harim is toward the regions with higher conductivity coefficient and specific yield. According to the values of hydraulic conductivity and specific yields, the role of hydraulic conductivity coefficient is more significant than the specific yield.

We also depicted hydraulic harim for the next 15 years, under the assumption of no changes in population, groundwater exploitation and consumption. Figure 13 shows this area.
Figure 13

Expected hydraulic harim for Haji-Abad qanat in 2040.

Figure 13

Expected hydraulic harim for Haji-Abad qanat in 2040.

Close modal

The hydraulic harim extended about 500 m from the mother well in 2040. The extension of this area is near the regions that have higher hydraulic conductivity coefficients such as the upper reaches of qanat.

In this way, the calculation of the harim area is important for preventing some probable problems faced by many of our qanats. The hydraulic harim principle prohibits drilling a water well within a specified distance of another water project, which is the main traditional law to prevent qanats from drying out. And this is achieved just with the help of simulation techniques, such as the accurate one. As such, the findings of this study can be applied to all types of aquifers and qanats, which are subject to varying conditions, as well as to arid aquifers that harvest water using this traditional method.

As a result, a comparison is carried out between the proposed model and other empirical equations like the Sichardt equation and drainage channels for hydraulic harim depiction of a qanat system. Table 6 presents the advantages and disadvantages of the proposed model in comparison to empirical equations.

Table 6

Comparison between the proposed model and empirical formulas in hydraulic harim depiction

AdvantageDisadvantage
Applicable for both steady and unsteady state High computational cost 
Considering different values of hydrodynamic coefficient near that qanat system High runtime 
Higher accuracy  
AdvantageDisadvantage
Applicable for both steady and unsteady state High computational cost 
Considering different values of hydrodynamic coefficient near that qanat system High runtime 
Higher accuracy  

The proposed model is applicable to both steady and unsteady states. It considers different values of hydraulic conductivity coefficient and specific yield near the qanat system, however, in empirical formulas, only one value can be entered into the equation. Also, as the engaged model, first, simulates groundwater flow and then depicts the hydraulic harim is more accurate than the empirical equations.

The only disadvantage of the proposed model is the high computational cost. Due to the heavy computation of this model, the runtime is much higher than empirical relations. The reason is solving a set of algebraic equations in MATLAB software.

In arid and semi-arid regions, qanat systems are used to collect groundwater. Qanats that drain water from aquifers have borders around them named hydraulic harim. Investigating this area in order to protect qanat from changes in flow rates and quality risks is critical and necessary for all qanat systems. Hence, in this study, we aimed to achieve the hydraulic harim of qanat by using a precise numerical method named meshless local Petrov–Galerkin. This is the first time it has been done. For this purpose, two aquifers, one standard and one real field aquifer, are chosen. Then, the qanat package has been added to the MLPG groundwater model. Finally, hydraulic harim is computed for the qanat. In the standard aquifer which has one mother well, three shafts in the collection section and three shafts in the conveyance section, harim is depicted. Hydraulic harim is drawn for 30, 60 and 120 days after exploitation. The hydraulic harim shapes for the three time periods are different. The length and width of harim for 60 days are greater than those for 30 days. Harim for 120 days is also larger than both 60 and 30 days. This is due to the high drawdown value for 120 days. Harim retains its constant shape after 120 days due to the equilibrium condition that governs the aquifer. Haji-Abad, one of the most important qanats in Birjand, is chosen for the real test case. Its mother well has a depth of 75 m. It has 10 shafts in the collection section. The hydraulic harim for this qanat is determined after 3, 6 and 11 years after extraction. Results show that the harim has expanded over time because of more extraction and drawdown. For instance, the length of hydraulic harim after 3, 6 and 11 years are 400, 700 and 900 m, respectively. The width of harim for these years varies from 200 to 300 m as well. This area is also larger for the mother well in comparison to other collection shafts. This is due to the high amount of water drained from the mother well. Results indicate the harim's development towards regions with a higher hydraulic conductivity coefficient. We also predict the hydraulic harim for this qanat 18 years down the track and find some buildings will be built in that area, and the qanat may face some problems. The length of harim this year is 1,700 m.

The authors want to thank the regional water company of South-Khorasan province according to providing the sufficient data.

All relevant data are included in the paper or its Supplementary Information.

The authors declare there is no conflict.

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