Achievements

THE ANALYSIS OF HYDROGEOLOGICAL-ENVIRENMENTAL PROBLEMS AND DIVISION OF PROTECT REGION IN SHANXI KARST SPRING AREA

Updated :11,15,2012

Liang Yongping, Han Xingrui, Yi Lianxin, Wang Weitai

Karst Geological Institution Of Chinese Geological  Academy

Abstract: The article aimed at Shanxi karst springsdischarge seriously decay in recent years, according to the water resource theory, through the research of the 18 karst spring areas(Fig-1 Jinci spring area, Lancun spring area, Shentou spring area, Niangziguan spring area, Xin’an spring area, Guozhuang spring area, Pingshang spring area, Majuan spring area, Longzici spring area, Huoquan spring area, Sangu spring area, Yanhe spring area, Tianqiao spring area, Liulin spring area, Gudui spring area, Hongshan spring area, Shuishengtang spring area and Leimingsi spring area, )water resources system structure model, the constitution of water resource elements and the circulatory process. Analyse the springs frangibility and why the springs discharge was decay from two aspects: natural and artificial.And then take this as a foundation footing and protect the springs as a intention.According to groundwater exploitation and coal mine exploitation affected to the sensitivity of springs discharge, divided the spring area into several protect regions with different rank,and also put forward different protective suggestions to every different rank.

Key words: Shanxi, Karst spring, discharge decay, divide protect region

 


Shanxi province has the widest karst area in Northern China and its karst groundwater was also the most abundance in Northern China. There has 86 karst springs which discharge more than 0.1m3/s,and 18 of them discharge more than 1 m3/s. The total discharge was amount to 88.2---107.8 m3/s.These karst springs has very vast drainage area,and their recharge,runoff, storage,discharge process was independent with each other, and these karst springs also had gigantic undergound regulating storage, centralized drainage. So, these springs has the advantage to estabilish large-scale water-supply source. Karst-water here does not only provide production, living and water-supply source in most cities,but also, lots of these karst springs has its special history and culture,were very famous places of interest. So, karst-groundwater played a very important role in peoples daily life, industry, agriculture, energy base and cultural construction.But,since 80s in 20 century, because of natural factors, mankinds activities and other disadvange influencing factors, there occurred series of hydrogeological environmental problems such as: discharge decay,water quality contamination, groundwater level descendant,and among all these problems:discharge decay was the most serious problem. It does not only deteriorate the sitution that Shanxi is lack of water resource, but also led to great harm to ecological environment and tourism resources.

Trend and Reasons of Discharge Decay



Fig-2 was a dynamic state curve of the 15 karst springs’ discharge in Shanxi province.the graph shows us that:from 1950s to the middle of 1960s, discharge had been fluctuated horizontally, but after the middle of 1960s, this data appeared a obvious decay tendency.The discharge of the 15 springs had been decreased gradually with the speed of 1.01 m3/s annually. Divided the 1956-2003 series into two stage ( the first stage:1956-1979, the second stage stage:1980-2003 ), The 15 springstotal average discharge reduced from 72.97 m3/s in the first stage to 42.36 m3/s in the second stage,and the reduced quantity shared 32.25 of the total average discharge in the first stage.Till the year of 2003,the 15 springs total average discharge have already been reduced 52.13 compared with the first stage,there are three springs (Jinci spring, Lancun spring and Gudui spring ) were completely setting off, two (Guozhuang spring and Hongshan spring ) were nearly with a zero flow,and there are six ( Niangziguan spring,Shengtou spring, Xin’an spring,Liulin spring and Shuishengtang spring )which average discharge reduced more than 40compared with the first stage,other three springs (Pingshang spring, Majuan spring and Tianqiao spring ), their average discharge reducement was below 30 compared with the first stage.

Why all these springs discharge were decayed can conclude into the following reasons:

1 Precipitation amount was decreased and evaporation on land was increased

By the contrast between the two stage in 156 precipitation station belong to the 18 springs.Compared with the first stage, all the springs universally decreased 3.5-14.38,and the total average evaporation reduced 8.26.According to temperature data and use Turkˊs empirical formula about evaporation on land: because of temperature-increase leads to penetration decreased amount was about to 49.

2 Influence go with exploit karst groundwater in spring area

By the karst-groundwater exploitation quantity data in 16 spring areas(except the quantity in the spring head), the average exploitation quantity was 3.3 m3/s in the first stage,and this data reached to 12.19 m3/s in the second stage.And till the year of 2003, the total exploitation quantity have been attained 17.75 m3/s in all the 16 spring areas,this data was 4.4 times more than the quantity in the first stage,and this data was 29.3 of the total available resource quantity.Nevertheless,there are declogging in coal mine which belong to Majuan spring area, Jinci spring area, Hongshan spring area, Guozhuang spring area and Niangziguan spring area.

3 Water-sourroundings change affected to discharge

Most of Shanxi’s karst-spring systems were so complex that include several water resource factors,and when other water resource quantity varied,the karst-groundwater quantity would also changed.Mankind’s activity affected to water resources in spring area is always all-around. The exploitation of coal mine, other types of water resource’s exploitation in the spring area,construct dam and reservoir, hold up surfacewater, all these actions will reduce the seepage recharge from river to karst groundwater.The report of surfacewater evaluation show that: compared with the first stage, river runoff decreased 36.28 in the second stage.By the compute in Niangziguan spring area,the seepage quantity that decreased because of surfacewater reduce was 0.84 m3/s. Compared with the first stage, Lancun spring and Longzici spring etc were not the type of all-out springs, so, when exploited groundwater in loose alluvium at Xizhang, Taiyuan. Tumen, Linfen, the direct  result was that the discharge of karst-groundwater decay.

4 Use of land

Exploitation of coal mine were universal among all the spring areas, large-scale exploitation have last more than 20 years not only change runoff producing condition on the ground surface,but also destroyed the clastic rock aquifer’s system structure in spring areas. According to the water resource evaluation report(the 2th time):the variety of the hydro-underlying-bed was the most important reason led to the decay of river runoff quantity in Shanxi province. Land use by traffic,housing and factory change part of infiltration recharge area into zero-infiltration area, resulted in the replenishment by precipitation seepage decreased.Take Yangquan city as a example, its total square is 4578 km2, till the year 2000, there are 20km2 used by traffic and 283 km2 used by construction,the two items sumed up together was more than 300 km2. And, a great deal of mine water was full of dusty coal flowed into the river directly over many years. These tiny coal particulate deposit gradually in the process of runoff,and accumulated for a long time.At present time,there are already a deposition layer which depth at 10-20 cm on the river bed, formed a layer that made a bad infiltration condition on the river bed,and the layer also decreased the seepage quality that from river to groundwater.

 Frangibility analysis of the springs’ discharge

1 The water resource system characteristics of  karst-spring area in Shanxi

To understand the water system characteristics from system angle, karst-spring areas in Shanxi have the following aspects:

Karst-groundwater system here is integrated and cosmically. The karst-groundwater aquifer in Shanxi constitute mainly by continuous deposit, very thickly carbonate rock (normally with a depth of 7001000 m ) belong to early Paleozoic Era.Geological structure is mainly made up of  large-scale anticlinorium, synclinorium and rift. The essential geological condition cause the karst-groundwater circulated with the independent spring area as a unit and the unit has its integrated system.The water-collecting area of the unit from severeal thousand arrive around ten thousand square kilometers, and the average area of the 18 spring fields was 3746 km2.

The karst-groundwater system has lots of water resource elements and the conversion relations among the elements were complex: Most of the system exist atmospheric precipitation, surfacewater, loose  alluvium pore groundwater, slastic rock crevice groundwater and karst groundwater, etc at the same time. And there are different kinds of complex conversion relation among all these water resource types, it made factors that affected karst groundwater increased and water surroundings quality frangibility.

A karst spring field always belong to differenf distracts (different country,city or province ) and different water user at the same time. And several kinds of intake projects functioning parallel increased difficulties to admeasurement and management of water resource.

Most of Shanxi’s karst groundwater were “water-coal coexist system”, karst groundwater always with closely relationship to mine, energy industry with heavy pollution and high water consume and coal chemical engineering industry. Consequently, series of water surrounding problems such as the lack of water resource and water quality pollution were serious.

2 The water resource system structure type and characteristics of the spring areas in Shanxi.

The hypsography of Shanxi can conclude to “ two mountain and one valley ”. Its region geological structure was mainly donmainated by the anticlinorium of Lvliang mountain in the northwest, the syncline of Qingshui in the southeast and Fenwei graben valley in the middle. The discharging  datum level was controlled by Yellow river valley on the east of Shanxi,Fen river valley in the middle and the North China plain on the east.So,most of spring fields’ discharging area were formed at these place.

According to the system structure of karst groundwater and relations between karst aquifers and the stream set of groundwater.We divided the karst water resources into three types: “ Inverse place type”, “Fluently place type” and “others”

(1); The system model of “Inverse place type” .

This kind of model mainly distributed at Taihang mountain area on the southeast of Qingshui syncline and a little  distributed at the southeast and southwest of Lvliang anticlinorium. The mainly characteristics of this type were:

1>  The whole stream set of karst groundwater was rightabout to the aquifer dip.The dominating regional geological structure was spring area located at one side of the syncline.Because of the central of syncline aquifer which cover up deeply cause groundwater movement suffocating. Consequently, the groundwater  movement was converse to the tendency of stratum,and drained at the place where have appropriate geological and topography conditions.

2>  The late Paleozonic Era and Mesozonic Era clastic rock stratum distributed at the up stream of the groundwater system. The mainly nourishment source of karst groundwater was composed of surfacewater that originated from these clastic rock area.

3>  The groungwater recharge area distributed at the lower reaches of the spring,and enriched at the shallow department where the Ordovician and the coalsystem stratum get in touch with,and here always formed surf-runoff zone.

4>  The drainage of groundwater was formed because of water-tighting of regional confining bed. Especially for the reason that the relative insulation by limestones at the bottom of middle series of Ordovician system and under Ordovician system series, The distribution of springs were disperse.

(2); The system model of “fluently place type”.

The water resource system of this model mainly distributed at the east of Lvliang mountain,the edge-mountain of the rift basin in Fenwei graben,the southeast of  Lvliang mountain anticlinorium.The mainly characteristics of this model were:

1>  On the transerve section,the move direction of groundwater was congruously with the stratum incline.Its geological structure foundation was groundwater circulated in amonocline on one side of the anticline.

The late Paleozonic Era and Mesozonic Era clastic rock stratum distributed at the downstream of the groundwater system. So, there always spreaded artesian areas of karst groundwater.

2>  Karst groundwater can be enriched at the shallow department where the Obdovician and the coal system stratum get in touch with, the spring outlet before the breakage which on the front of mountain and artesian areas of downstream of spring outlet.

3>The draining of karst groundwater was formed because of the water-tighness of regional confining overlying beds or stratums under the breakage structure .

(3); “Others” model.

Other three spring areas: Gudui spring area, Shuishengtang spring area now can not be classified into any of the model. So, for the moment, we called it “others” model.

3 The analysis of influence factors to the karst spring’s discharge frangibility

The concept of trangibility to groundwater system was put forward for evaluated the capability that water-bearing system resisted contamination.The spring’s discharge frangibility we discuss today was put forward under the serious situation that karst springs in Shanxi were in the face of discharge decay or even setting off,and how to protected it under this situation. Any spring, when its recharge-didischarge was out of balance for a long time, setting off of the spring will be the logical result. But the development scale, structure of stratum, type of water-bearing media and the spring’s formation conditions of the water resource system was so different, and distribution, buried conditions,rules of enrichment and flow speed of karst groundwater were also different with each other. There are always zones in some spring that their discharge response mightness  towards outside functions. The influencing pace and intensity were visible when exploited karst groundwater in these places.Especially in some sensitive places,a number of wells may cause the spring made a completely move.So,we defined the frangibility of spring discharge in spring area as: the sensitivity degree of spring discharge in spring area to outside force under the influence of outside environment. The discharge of the spring more frangibility means that  the spring was more and easily  affected by the influence of outside activity. The mainly conditions that affected the discharge frangibility of spring were:

1 The spring area growth scale is small and supply resource amount is limited, a little amount of mine may cause the spring dried up. Such discharge of spring areas is tender.There are 5 in all the 18 spring areas which acreage below 1000km2.These springs were; Leimingsi spring area, Hongshan spring area, Majuan spring area,Shuishengtang spring area, Gudui spring area, and two of them were setting off.

2 There are artesian provinces of karst groundwater enrichment zone, and less enrichment zone of artesian coal mine area. Dill wells to get water at these place equal to incerpted spring water directly,it will leads to discharge decay easily.And excavate mine in the artesian coal mine area,once coal mine suddenly occur declogging will cause discharge decay directly too. Spring areas with such characteristics were: Liulin spring area, Tianqiao spring area, Hongshan spring area,Jinci spring area, Leimingsi spring area, Guozhuang spring area,Huoquan spring area, and these spring areas were all “ fluently place thpe” system model.

3 The discharge of spring areas controlled by fracture zones. Although these fractures have water-tighness on its transverse section,but in Shanxi, these fracture zones which formed spring discharge were all located on both side of Fenwei graben. They were not only tension faults but also active faults. Water transmissibility along these faults was comparatively strong. So, these fracture zones were sensitive areas which have great effect to the discharge of karst spring water.Spring areas have such characteristics were: Jinci spring area, Lancun spring area, Hongshan spring area, Longzici spring area, Guozhuang spring area and Shengtou spring area.

4; Strong-runoff  zones of karst groundwater was developed .The karst growth degree was deficient in Northern China,But in some large-scale spring areas, through a very long time karstification,affected by the following factors:the lithology of aquifer,structure, environmental geology background,ancient karst,hydrodynamic and other influencing factors,finally formed strong-runoff zones of karst groundwater. These strong-runoff zones had such characteristics: transmissibility was relatively better,water volume was abundant, single well has agreat water crop,and reflected in the chart of hydroisobathwas a flute.Some large-scale runoff zones even with a length of several ten kilometers long. and connected directly with the spring out let.So,when exploited karst groundwater in the strong-runoff zone,there will be obvious infection to the discharge of fountain.By prospecting and analyse the hydroisobath,it can be affirmed that spring areas with strong-runoff zones include:Niangziguan spring area,Xin’an spring area , Sangu spring area, Yanhe spring area,Jinci spring area, Tianqiao spring area,Liulin spring area, Guozhuang spring area and Shentou spring area.

5: The centralized degree of the fountain discharge.


Table-1 Analysis table for single factors of frangibility

SPRING AREA

TYPE

SCALE

GRAVITY FLOW

FRACTURE ZONE

STRONG RUNOFF ZONE

DECENTRALIZATION

Niangziguan

INVERSE

PLACE

TYPE

large

nonexistence

no

have

dispersed

Xinan

large

nonexistence

no

have

dispersed

Yanhe

middle

nonexistence

no

have

dispersed

Sangu

middle

nonexistence

no

have

dispersed

Pingshang

middle

nonexistence

no

unknow

dispersed

Majuan

small

nonexistence

no

unknow

dispersed

Longzici

middle

nonexistence

yes

unknow

centralized

Shentou

FLUENTLY

PLACE

TYPE

 

middle

existence

yes

have

dispersed

Leimingsi

small

existence

no

unknow

dispersed

Lancun

middle

existence

yes

none

centralized

Jinci

middle

existence

yes

have

centralized

Hongshan

small

existence

yes

unknow

centralized

Guozhuang

large

existence

yes

have

dispersed

Huoquan

middle

existence

yes

unknow

centralized

Liulin

large

existence

no

have

centralized

Tianqiao

large

existence

no

have

dispersed

Shuishentang

OTHERS

 

small

nonexistence

yes

none

dispersed

Gudui

small

nonexistence

yes

unknow

centralized


The formation reasons of karst springs in Shanxi can conclude as two types: the erosion-overflowing spring because of the water-tighness of the confining overlying bed and the contact-overflowing spring because of water-tighness of fault. Seen from the Fig-3 and 4:discharging of springs with the first formation reason was always decentralized,and springs with the second formation reason, its discharge was always centralized. Generally speeking, the distribution of fountains more disperse, their recharge routes will accordingly more disperse, and the discharge frangibility of spring was also more lower.

Marshal the influencing factors of discharge frangibility in the Table-1,we can conclude that the discharge frangibility of water resource system in “inverse place type” was lower than the type of “fluently place type”. 

 Partition of the protection regions  about fountain discharge

The aim to protect the discharge of fountain was to maintain the spring output on a certain amount, that the amount could be able to satisfy the water supply need,at the same time, the amount could also bring into play its tour, ecology and other functions. Consequently, in the process of development and programming, we should take the exploitation amount of resources as a foundation, practice a total amount control, play discharge of spring and exploitation amount of karst groundwater in different region belonged to the same spring area as a whole.According to the characteristics of different spring areas,divided protection regions of fountain discharge as the following Table-2and Fig-5.

  1 Protection regions of spring head

Protection regions of spring head means drainage districts of karst groundwater which was revealed. The total area of the 18 protection regions of spring head divided this time was 222.58 km2 which is share 0.33 of the 18 spring areas’total area.It was forbidden to drill wells, dig springs, cutoff and divert water without permission,coal mining, exploitation of mine, quary and construct projects underground were alao should be prohibited, other construction items which were irrelevant with



water supply establishment and protect the spring head should not br set up lately,rebult and enlarged. Advocate to get water by collect fountain instead of drilling wells in the spring head.Strengthen the protection of natural sight and historic architecture in the spring head.

  2 The first-rank protection region in spring areas.

The first-rank protection region in spring areas were mainly aimed at places where are sensitive to the influence of discharge. These regions include: fracture zones in front of mountain which formed springs, artesian regions under the spring outlet which were closely related with discharge of springs, strong-runoff zones of karst groundwater which discharge amount approach to minimum target value. There are 11 among all the 18 spring areas exist prior-protective regions of water quality. The total area is 1579.96 km2 which is share 2.29 of the 18 spring areas’ total area. The mainly safeguard in the first-rank protection


 

 

 

Table-2      Area statistics of protect regions          km2

   ITEMS

 

 

SPRING AREA

TOTAL AREA

SPRING HEAD

FIRST RANK

SECOND-RANK

SUBLAYER-COAL BEARING COURSE REGION

JINCI

2030.00

2.06

183.35

243.46

601.76

LANCUN

2500.00

3.77

178.88

73.91

76.05

NIANGZIGUAN

7226.72(9.72)

13.87

222.05

1107.95

2544.68

XINAN

10950.00

16.07

0.00

1627.00

6826.19

SHENTOU

4756.00

10.18

43.53

349.79

842.85

GUOZHUANG

5600.00

9.33

374.48

1387.29

1363.49

GUDUI

460.00

5.04

0.00

0.00

92.60

LIULIN

6080.54(78.05)

2.08

221.7(51.61)

261.55

1595.27

YANHE

2765.00

40.04

0.00

284.20

642.71

SANGU

2630.00

27.31

178.80

391.45

97.79

PINGSHANG

3035.00

10.31

0.00

0.00

0.00

MAJUAN

754.00

1.15

0.00

44.96

239.46

TIANQIAO

13591.48(3399.48)

33.86(11.34)

0.00

17.13(4.47)

808.46

HONGSHAN

632.00

1.92

70.10

82.30

72.82

LONGZICI

2250.00

11.20

19.90

24.87

0.00

HUOQUAN

1273.00

2.30

35.49

1235.21

199.79

SHUISHENTANG

518.00

9.24

0.00

0.00

0.00

CHENGTOUHUI

1672.00

13.68

0.00

0.00

0.00

LEIMINGSI

377.00

22.85

51.69

228.89

28.13

Σ

67428.74(3487.25)

222.58(11.34)

1579.9751.6

7359.96(4.47)

16032.05

Note in()was area out of shanxi province


region include: Except the situation that water is used by people and livestock drinking or other spectial use,and there  are not other water sources.

 exploitation wells and exploitation amount pertinent to karst groundwater and pore groundwater in loose layers which have close relation to karst groundwater should not be set up lately. For the water sources have already established,we should gradually decrease the exploitation amount if there are substitutable waterhead. Coal mining under the karst groundwater level should be sternly controlled in the protection region.

  3 The second-rank protection region in spring area.

The second–rank protection region mainly aimed at strong-enrichment zones of karst groundwater (strong-runoff zones, water-collecting region )and the whole distribution region of karst groundwater in some spring area which needs spectial protect.Karst groundwater in these places are abundant,single-well has great water crop and transmissibility was relatively better.Dill wells at these places will leads to great  



Fig 5 The distribution map of discharging protective zones in Shanxi


 


influence to the amount of discharge, and the respond of time was quickly.

  There are 15 among all the 18spring areas exist limited protection regions of water amount.The total area is 7359.96 km2 which share 10.92 of the total area of 18 spring areas.Actions related to drill well and increase exploitation amount in the limited protection region should be examined and approved strictly.

  4 The region in coal mine that its sublayer-coal is bearing course

Regions that the distribution of sublayer-coal under the karst groundwater level in spring area. There are 15 among all the 18 spring areas exist such regions (a part of Tianqiao spring area that out of Shanxi is lack of credible date ).The total area is 16032.04km2 which share 23.78 of the 18 spring areas’ total area.Exploited coal in the bearing course under the karst groundwater level must be carry strictly argumentation of hydrogological condition, and examined and approved by the water resource administration department that hyper-city-grade.

Conclusions

Karst springs in Shanxi had the universal trend of discharge decay in recent years, and this situation seriously threatened the development of agriculture, industry and ecological construction. The article according to the constituent, structure and circulatory characteristics, take the reason of discharge decay as afoundation,and protect springs as a aim, dividede the spring area into several protection regions with different rank, which include protection region of spring head, first-rank,second-rank and coal mine bearing region in the spring area. And put forward corresponding protective suggestions to provide scientific gist for management and protection of karst groundwater.

Acknowledgement

This article was supported by “KARST AQUIFER AND WATER RESOURCE” (IGCP513) project which was supported by UNESCO and IGU.