Construction Challenges For Bridges In Hilly Area

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                       INTRODUCTION
Himalaya since Vedic times have been considered a vast repository of valuable medicinal herbs, minerals, forest resources etc. Vedic literature followed by the writings of Charaks, Susruta, Dhanwantri, Nagarjuna, Parashar, Balmiki and various other saints, bear testimony to it. "Alexander, The Great", who was much influenced because of its scenic beauty, bracing climate and agroclimatic conditions, made a great publicity of the Himalayan Herb Science in Yunan and Rome during middle ages (Anonymous, 1977; Chauhan, 1988). This potential, however, remained unexploited especially in higher reaches due to inadequate means of communication. After independence, Govt. of India, gave a special emphasis on road construction in order to bring socio-economic upliftment of tribal inhabitants. But due to lack of proper planning it resulted in serious ecological imbalances.
Society has now become aware of the environmental consequences resulting from road construction in hill areas. Right from the days of Vedas, our country has an age-old tradition of environment consciousness. During Samrat A shok is days social forestry was at its full swing having shady trees along the roads and fruit plants on the wastelands. In this paper efforts have been made to incorporate the latest techniques for protecting the environment after extensive survey of literature (Lone et al., 1992 and Chauhan
 Hilly region pose unique problem for bridge construction. In a restricted hilly area itself climatic conditions, geological features and hydrological parameters vary considerably. Keeping in view the bridge site and various constraints, type of bridge and method of construction are to be selected carefully for safe, economical and successful completion of bridge construction.
Various challenges that come across while constructing bridges in hilly area are
1. Construction of bridge across deep gorges
2. Construction of bridge on rivers with bouldary beds
3. Construction of bridges in extreme temperature zones
4. Construction of bridges on sharp turn on highway
5. Landslide or Debris flow
Deep gorges, rivers with bouldary beds, extremely low temperature condition, high winds, landslide etc. in hilly regions require special attention to complete the activities of bridge planning and construction in a systematic way and are discussed here in.

Bridge Construction Overview
Planning and monitoring is basically what is to be done in due course of time, and how it is to be executed in the planned/allotted period for the particular bridge. All the pros and cons of the likely problems in the anticipated period need to be examined. Also the records of important points are made available at site with executives as follows:
Why the particular site was selected for the bridge.
Why particular type of bridge is proposed. (structural arrangement)
Site data
Proposal for preparation drawing.
Soil strata in the form of bore log.
Model study detail if already done for scour assessment.
Salient features of the bridge and quantities of each items involved.
Upto date approved structural drawings.
Details of all meetings and up to date decision if at all taken.
Decision making mechanism in case of any dispute i.e. Dispute Review Borad (DRB) be already finalized.
Bridge Foundation and Substructure
Foundation construction for any large bridge takes time. Problems encountered during construction of foundation depend upon type of foundation, soil strata encountered, equipment/plant deployed and logistic problems. Construction difficulties anticipated during the execution be kept in view while planning the works/ period for the job. Foundation can be opened foundation, pile foundation, well foundation or any other types of foundation. In case of well foundation, the various type of soil are encountered and it becomes difficult to give any clear time schedule about the sinking of wells unless the soil details are very clear and the anticipated profile matched with the actual encountered. In case of bouldery and clayey soil the rate of sinking schedule is likely to be slow when compared with the sandy soil. Also there may be requirement of pneumatic sinking technique subsequent to open grabbing due to difficulties in sinking of well. As the cost of pneumatic sinking is very high, this should be deployed judiciously. In such cases, there is need to keep the details of all the sinking difficulties in a systematic order and this can be reviewed in consultation with decision making authority. Review of soil parameter if required be given more attention and wherever required the details may be referred to material testing laboratory but within the time schedule. This may be helpful to recommend revision in foundation level, wherever possible based on soil data report. Tough strata in the foundation stage should be considered as engineering friendly
Superstructure
For particular site there are numerous structural arrangements possible. Final proposal be made based on the greater examination of site condition may be technical, aesthetic and construction methodology. Special care need to be taken in case of deep gorge where there is sizable difference between soffit level and bed level. This may pose difficulties for staging and shuttering. Proposal recommended for site should be well read in advance. After the proposal has been finalized for particular bridge, the construction can be planned. The quantities of each items involved and execution method be listed. Basically method statement should be kept ready for overall execution including job estimate. This data will be kept to ensure smooth progress of project.
Management of Construction Activities
Management of bridge construction demands that construction manager to reorient all the resources in such a way that the project is completed without any time/cost over run. Output of the work depend upon how best the activities are managed which will vary from site to site based on many factors. Based on the experience, various aspects be identified for efficient construction management. Schedule of construction based Critical Path Method (CPM) be prepared along with major milestone and Bar Charts. Latest software management tool can be used for this in case of a major bridge project. Design of Bridge is a post sanction in case of departmental construction and after tendering action in case of bridges throughout contract. It is necessary that design must be preceded by at least six to eight months or say 50% ahead of execution of concerned event. It has to be ensured that this should be completed well in time. Reviseddesign if any should be updated and clarified without delay. Observation on the approved design drawing if any be passed to design office immediately to make the changes. This is most important in case of foundation where design soil parameter needs to be adhered to. These may vary on actual execution and require review of design. To keep details with design office it is necessary that progress of foundation work be well informed to the design office.
Plant Management
Requirement of equipment/plant be assessed systematically and accordingly action may be taken to arrange this for a particular job.
Quantum of work covering all the items with specifications
Time available for work excution
Details of equipment and also minimum requirement as per job position.
Rated capacity of equipment/ plant
Assessed capacity
Schedule of maintenance
Inventory of spare parts required
Repair cover to equipment/plant
The layout should ensure minimum movement of material, equipment and personnel of the area is an essential condition, for operation of some equipment for example tower crane operation not possible at heavy winds speed. Stone crusher if required for site should be suitably located. Supporting facilities such as generator, office, stores should not be located in the path of dust, flow. The service road should be properly maintained. Receipt and despatch of equipment be kept in proper format to keep of details of its utilisation at site.


After staff has reported at site necessary action should be taken to utilise all the equipment. The required facilities for servicing and repair must be established to meet requirements.
Material Management
Material management is a parallel activity along with start of the Project. This cover procurement of camp material, office equipment, major purchased items, such as aggregates, sand, cement, steel, structural steel, shuttering consumables, electrical fittings. Forecasting of quantities and cost of various items on monthly basis must be done at least three to six months in advance which should be regularly reviewed.
Finance Management
No project or project management can be meaningful without this. In case of Government work the manager should get his budget fixed on monthly basis, on the basis of work done or minimum to be fed at site, on the decision of higher authorities. Key to measure financial planning lies in taking all above action and taking suitable measures at appropriate times to ensure that individual inputs are achieved to the maximum and capital investment kept at the lowest level.
Quality Management
Quality of work at site is most important activity and manager should always grapple to improve the same. Training to staff should be provided to update the quality control measure and it should become part of the work culture. At site laboratory be established to check the quality of concrete.


Tests be analysed at site based on the size of job. Mix design should be prepared based on the latest code and to produce the concrete of desirable strength. Compaction of concrete be given more attention before final setting. Latest guidelines issued by IRC and MORT&H be followed for systematic quality assurance. Quality assurance on ground improve the aesthetic of structures.
Safety Management
Safety of employees at site should be observed very seriously. All the workers be given briefing about the safety requirements based on the site hazards. Specially when the simply supported structure is attempted on deep gorge, suitable arrangement should be made to avoid any accident at site during insitu casting of superstructure. Also in case of foundation if the deep excavation is involved, the quality of surrounded soil be kept in view. There are incidents where few workers got buried in deep excavation due to sudden slide, this should be taken care. In case the well foundation is being attempted using double drum winch care need to be taken during grabbing process. During the diving process the proper coordination needs to be made between the diver and attendant to intimate about the problems if any, for which local signaling arrangements used, this can be finalised at site based on convenience. In case the pneumatic sinking is being used for well foundation, following safety measures, may be observed:
Accelerate circulation of air
Slow decompression
Duplicate and spare equipment
Illumination inside working chamber
Signaling arrangement
Caution about incidental loading
These precautions should be seriously followed to avoid any catastrophes at site. Safety management is also important in case on staging shuttering for superstructure. There are cases in the past where the collapse of shuttering/staging has led to loss of life. This needs check in before casting the superstructure. In case steel truss is being used as a staging arrangement, design and launching arrangement be thoroughly checked.
Documentation Management
Document management during the contract is an art in itself. Proper and systematic management of documents is utmost requirement for department as well as contractor. All the details should be property vetted by both the parties. Better documentation will avoid any disputes during the currency and after completion of contract (i.e arbitration cases areavoided). This needs special attention of the managers of both sides. Most of the cases being dealt by the arbitrator in our country, due to lack of understanding between two parties which, are further affected by improper documentation. In fact better documentation reflect the system of management in any project. Control estimate is required to be prepared annually to assess the job position. This should include work done till date and balance work in terms of money. This will be a guiding principle to progress the job in later period till completion. This practice is a must in all major bridge under construction. As project management has evolved, documentation has become a key skill particularly as projects become more complex and difficult. Organised documentation is the best defence against claims. Documentation that every project manager must have at their disposal are as under:
Proposal and Bid Estimates – These documents describe how the contractor envisioned the construction of the project and his plan to accomplish the work. It includes information about costs and schedule as well as construction methods.
Project Schedule - This is one of the most overlooked project records and it can provide the best documentation in a claim situation. The original baseline schedule sets the mark for monitoring the effects of any delays or unforeseen project disruptions.
Project Change orders – Any variances from the original contractual requirements must be documented and separated from the original scope of work requirements. Daily reports, time sheets, letters of correspondence and meeting minutes or any other documentation discussing agreements made between parties should be readily available.
Personnel Management
Manager should put the engineers, to activities they can perform better. Individual differences should be studied in detail to assign the suitable job to engineers, administration and account staff. Manager should be a good Psychologist to assign the work based on the inclination of the people at work. A considerable free hand be given to see what an individual can produce. He should be guided from time to time and work be kept on progress.


Decision making circulated, critical activities be cleared by manager after proper deliberations. Also care must be taken to select a new entrant suiting to the job for requirement.
Conclusion
With the changing scenario—there is urgent need to manage the bridge project effectively. Construction management basically is a tool to complete the project effectively within fixed amount but in less time. Manager should have knowledge sequence of all the activities. Decision making for both sides the contractor and the client needs to be fast and time bound otherwise the project will get delayed which will have cost over run. Control in form of reviewing monitoring has a catalyst effect to boost the progress.

PROBLEMS
There are a large number of ecological problems associated with road construction in hilly tribal areas, some of these can be summarized as below:

i) Deforestation: The association between deforestation and slope instability has been a subject of considerable research. Deforestation brings about erosion and soil movement is generally accepted, but opinions differ on its impact. So far as "Creeping" slopes are concerned, greater creep velocities are found in slopes covered by trees in the region of Queenland (Australia) than in slopes merely covered by grass in region of rain forests (Brown and Shen, 1975). Prandini et al. (1977) reported that deforestation leads to loss of mechanical strength imparted by rock system. Reinforcing power of roots is also demonstrated by the results of in situ block shear tests, which show that shear strength increases with increase in root density. At higher altitudes top green layer is very thin and takes hundreds of years to come. A large number of trees along the roadsides are falling down due to road construction. Improper road construction results in soil erosion that may lead to uprooting of large trees and degeneration of lower plants. This way it leads to serious ecological imbalances affecting adversely run-off factors, temperature gradient, surface radiation etc. Due to loss of vegetation, the velocity of run-off also increases that results in soil erosion, hence of soil-fertility.
ii) Disturbance of geological strata:Operations like blasting excavation, chipping of mountain slopes to come to desired accessibility, are involved during road construction in hill areas. These operations creates geological disturbance in the mountain body. The blasting operations set dynamic forces causing the movements of slip zones, cracks, fissures and weak planes. The geological havoc caused due to road construction in Kinnaur District in before us. The chronic problems of landslides at Tranda, Chaurah and Kadhra dhank are a few examples.
iii) Hill face disturbance: Natural inclination of hill face is disturbed by road cutting operation. Down hill movement of the land slides material and disposal of excavated mass from road construction degrade and deface the nature. Growth of vegetation is affected by the loss of topsoil that causes ecological imbalances.
iv) Drainage pattern interruption: Velocity of run-off at the down hills increases to a very large extent due to construction of bridges and culverts on the road as well as due to cutting for getting proper communication systems. This leads to eroding of banks and is a threat to the existence of trees and vegetation on the hill slopes. Sometimes lakes are formed by accumulation of debris from the excavated material and land slides. Such lakes formed force the water to flow through some other way destroying the side by flora e.g. at Nallah on NH = 22, bridge was washed away thrice in six years because due to debris river was blocked and a temporary lake was formed. Same story was repeated at Pabbar river in Chhawara valley (Rohroo) in 1992, where a big lake (2 miles) was formed and about ten villages were vacated in order to avoid any loss to human life. This lake formed resulted in a loss of large number natural wealth both flora and fauna. This way natural drainage pattern of the area is disturbed by road construction, which sometimes results in flash floods also.
v) Water resources disturbance: Natural water resources get disturbed due to blasting which is used during road construction activities. Moreover, improper disposal of fuel, lubricants used in the process contaminates the surface and ground water.
vi) Siltation problem: A large quantity of excavated material disposed on the down hill slopes is carried by the river that gets accumulated in the dams and reservoirs and reduce their life-span e.g. siltation rate of Bhakhra Dam reservoir is very large which is due to large scale road construction in Sutlej catchment.
vii) Destruction to flora and fauna:Wild life gets disturbed due to blasting, hauling of machineries, shriveling sound of road rollers and noise of moving vehicles on the up-gradient. Destruction of key habitats such as resting sites, hollow trees, feeding and breeding grounds occurs due to road constructions. Some of the flora and fauna gets destroyed out right due to intrusion into forest for road construction.
viii) Pollution: Tremendous pollution is created due to accumulation of debris down hill. Moreover, heating of bitumen through hot mix plants produces a large number of air pollutants like oxides of sulphur, nitrogen and carbon. Long chain aliphatic hydrocarbons and aromatic compounds are also the byproducts of this heating process, which are having carcinogenic property (Cancer producing) and special precautions must be taken for protecting the labourers working under such conditions on the road construction site. Surrounding temperature gets increased and atmospheric humidity is lowered due to movements of machineries and vehicles, altering the physiological processes of the plants and thereby affecting their growth pattern. The alterations in the surrounding conditions causes interference of micro-organism life in the soil.
ix) Destruction of medicinal wealth:In the hill areas of Himachal Pradesh out of 3000 species of identifies plants, over 500 species possess various kinds of medicinal properties. Hundreds of plants have ethno botanical importance. There are about 150 species of aromatic plants used in different kinds of cosmetics and having different medicinal properties. But due to improper planning in road construction and processes involved during road construction, the natural wealth gets destroyed costing crores of rupees in spite of protecting the atmosphere from pollution.
PROTECTIVE MEASURES
In order to maintain balance between the road construction activities and environment certain protective measures have to be taken. Some of these measures are as follows:
i) Environment impact assessment: Before starting the road construction operation, environmentalists must be consulted in order to avoid any ecological imbalance.
ii) Geological investigation: A geologist must be incorporated in the road construction work. Blasting and chipping of mountain slopes must be done under his instructions in order to avoid any geological havoc.
iii) State of wildlife: During the road construction loss to flora and fauna must be minimum. It should not be disturbed. An environmentalist must be consulted prior to road construction work.
iv) Avoidance of unstable and fissureal zones:Roads should not be constructed in lose soil and where erosion chances are more. In such cases the help of a soil Engineer must be taken, before starting any such activities.
v) Least disturbance to natural streams and gradients:Natural face of the hill must be least disturbed while constructing the roads. Only the required land must be used for the purpose.
vi) Restriction on reserve forests: Road construction activities must be minimum on reserve forests in order to avoid any disturbance to natural wealth. This will help in maintaining the ecological balance.
vii) Judicial way of doing work: While cutting and disposing the debris special care must be taken so that there is no soil erosion and loss to flora and fauna.
viii) Minimum blasting operations: Blasting practice during road construction must be to the minimum extent in order to avoid any dynamic forces causing movements of slip zones, cracks, fissures and weak planes.
ix) Half tunneling must be restored:In case of vertical rocky slopes half-tunneling must be restored.
x) Ropeway technique: In case of less densely thick population ropeway must be installed instead of going for road construction. This will provide protection to soil erosion, wild life and environment.
xi) Suitable drainage system: Along the entire side of the road, a suitable drainage system must be provided so as to avoid any flash flood, soil erosion, damage to vegetation etc.
xii) Restoration of natural springs and waterways:Natural springs and water resources must not be disturbed during road construction process, otherwise it will be a great challenge to the nature.
xii) Rebuilding of environment:
a) On suitable points, places must be provided that may act as scenic spots to the users.
b) Programme of social forestry must be taken upto the root level. The wastelands must be garlanded with trees, and valuable herbs and shrubs. The best example of social forestry is found in china where even single inch of wasteland is not left without plantation. Debris obtained during road cuttings must be accumulated at some appropriate place and plantation must be done on the same. This plantation will help in retaining the natural environment.
c) Plantation must be done along the banks of rivers, nallaha etc. in order to avoid any further cutting of soil and to protect the water reservoirs and dams from more siltation.
d) Small water tanks along with the proper drainage system must be constructed along the roadsides in order to protect both flora and fauna. Roadsides must be planted at war-level so as to give the best example of afforestation.
CONCLUSION
Although road construction in hilly areas causes a huge damage to both flora and fauna in spite of having adverse effect on environment, but without proper communication facilities, it is not possible to explore the valuable wealth of such areas. So a balance must be struck between the road construction and environment in order to minimize the ecological imbalance. Certain scientific measures must be taken into account while constructing the roads in hills. The balance between the two will lead to the prosperity of the region and no hazard to environment will occur.

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GEOTECHNICAL CHALLENGES IN SLOPE ENGINEERING OF
INFRASTRUCTURES

Slopes within infrastructures sometimes slide and cause damage and inconvenience to the public.
Some of these landslides have claimed lives. Landslides include newly completed slopes, such as
the recent failure at Putrajaya as well as old slopes, such as the collapse of the rock slope of the
PLUS Expressway at Bukit Lanjan (2003), which was completed more than ten years ago.
The most notorious one was the collapse of a slope with rubble walls bringing down the Tower 1
Apartment of Highland Towers and killing 48 people on 11 Dec 1993. The towers were built in
1978.
A review of the causes of landslides indicates that most of the landslides are man-made slopes
and are mainly due to design deficiency (Gue & Tan 2006). This keynote also discusses some of
the recent and older failures, the causes of failures, and outlines some suggestions to mitigate
future occurrence.
Keywords: Slope Engineering, Infrastructure, Research & Development (R&D), Culture

1. INTRODUCTION

With the increased developments that have encroached into the hilly areas over the past two
decades, Malaysia experiences frequent landslides with a number of major slope failures which
cause damage and inconvenience to the public. These landslides include newly completed slopes,
such as the recent failure at Putrajaya in 2007 as well as old slopes, such as the collapse of the
rock slope of the PLUS Expressway at Bukit Lanjan (2003), which was completed more than ten
years ago. Some of these landslides have claimed lives. The notorious collapse of Tower 1
apartment of Highland Towers claimed 48 lives in 1993.
Climate conditions in Malaysia are characterized by relatively uniform temperature and pressure,
high humidity and particularly abundant rainfall with annual rainfall intensity over 2500mm.
Most of the landslides in two monsoon seasons of Malaysia are induced by the high rainfalls and
more than 80% of landslides were caused by man-made factors, mainly design and construction
errors. (Gue & Tan 2006)
Many will still remember the collapse of the Highland Tower on 11 Dec 1993. Since then, there
have been other major landslides resulting in fatalities and severe losses and destruction of
property. A brief discussion of these major landslides and their causes is presented here. This key
note also outlines some suggestions to mitigate future occurrence.
1 CEO, G&P Professionals Sdn Bhd & Managing Director of G&P Geotechnics Sdn Bhd Kuala Lumpur, Malaysia
2 Associate, G&P Geotechnics Sdn Bhd, Kuala Lumpur, Malaysia

2. MAJOR LANDSLIDES IN MALAYSIA

Among the major landslides occurring in the past two decades, the most notorious landslide was
the collapse of a slope with rubble walls, bringing down Tower 1 Apartment of Highland Towers
and killing 48 people on 11 Dec 1993. The towers were built in 1978.
Major landslides occurring within infrastructure seldom result in loss of lives compared to those
occurring in residential areas. However, major landslides that occurred within infrastructures
have resulted in great economic loss to the public and business due to disruption to the
transportation network and property damage.
The following table summarises some of the major landslides with their consequences: -
DATE OF
OCCURENCE
LANDSLIDE
LOCATION
(NAME)
CATEGORY FATALITY
(NOS)
DISRUPTION TO
TRANSPORTATION
NETWORK
11 Dec 1993 Highland Tower Residential 48 No
20 Nov 2002 Taman Hillview Residential 8 No
26 Oct 2003 Bukit Lanjan Highway - Yes
12 Oct 2004 Gua Tempurung Highway 1 Yes
23 Mar 2007 Putrajaya Public
Amenities - No
13 Nov 2007 Pulau Banding Public
Amenities - No
Table 1: Major Landslides with their Consequences in Malaysia
(After Abdullah et al. 2007)
2.1 Collapse of Tower 1 of Highland Towers Apartment, 1993
The Highland Towers Condominium is located in the district of Hulu Kelang, Selangor. Highland
Towers consisted of three blocks 12 storey high apartments named simply Block 1, 2 and 3
respectively. It was constructed between 1975 and 1978. Block 1 was completed and occupied in
1979. Tower 1 therefore collapsed 14 years after completion.
Figure 1 shows the water path before and after the completion of the Highland Tower
Apartments. In the course of the Highland Towers development, the stream was diverted by
means of a pipe culvert to flow northwards across the hill slope directly behind Highland Towers.
The approved drainage system on the hill slope behind Highland Towers was never completed.
Figure 1 shows the water path before and after the completion of Highland Towers.
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Aerial Photo 1975 (Before Completion) Aerial Photo 1993 (After Completion)
Figure 1: Water Path Before and After Completion of the Highland Towers Apartments
On Saturday, 11 Dec 1993, at about 1.30p.m., after 10 days of continuous rainfall, Block 1
collapsed and killed 48 people. The cumulative daily rainfall intensity measured from 1st to 10th
December 1993 recorded at JPS Ampang was 177.5mm and the measured maximum daily
rainfall intensity was 59.5mm. It was not exceptional rainfall as compared to previous measured
rainfall intensity.
An investigation was carried out by experts and specialists assembled by Majlis Perbandaran
Ampang Jaya (MPAJ) and was published in a report titled “Report on the Inquiry Committee in
the Collapse of Block 1 and The Stability of Blocks 2 and 3 Highland Towers Condominium,
Hulu Klang Selangor Darul Ehsan” in 1994. The report concluded that the most probable cause
of the collapse of the tower was the buckling and shearing of the rail piles foundation induced by
the movement of the soil. The movement of the soil was the consequence of retrogressive
landslides behind the building of Block 1.
The landslide was triggered by inadequate drainage on the hillslope that had aggravated the
surface runoff (MPAJ 1994). Slope and rubble walls behind and in front of Block 1 were also
found to be improperly designed with an overall Factor of Safety of less than 1. Figure 2 shows
the sequence of retrogressive failures that took place, causing large soil movement and piling up
behind Block 1 and causing an increase in lateral pressure to the foundation of the building and
the rubble wall in front of the Block until it collapsed and was followed by the toppling of the
apartment. Figure 3 shows the collapse of Block 1 of the Highland Tower Apartments.
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Figure 2: Illustration of Retrogressive Slope Failure Sequence (after Gue & Tan 2002)
Figure 3: Collapse of Block 1 of Highland Towers Apartments, 1993
2.2 Collapsed Bungalow at Taman Hillview in Ampang, 2003
The collapse of a double storey bungalow at Taman Hillview in Ampang (Figure 4) occurred on
20 Nov 2002 and claimed 8 lives. The cause of landslide at Taman Hillview was similar to the
Highland Towers tragedy, where failure of a rubble wall again triggered a landslide. The Factor
of Safety of the rubble wall in the Highland Towers was found to be less than 1.0 even without
Reduced Level (m)
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considering any presence of geological features such as relic joints etc and water tables. In fact,
the rubble wall is part of the series rubble walls behind Highland Towers.
Figure 4: Collapsed Bungalow at Taman Hillview in Ampang, 2003
2.3 Rock Slope Failure at Bukit Lanjan, 2003
On 26 Nov 2003, a massive rock slope failure occurred at Bukit Lanjan Interchange which is part
of the New Klang Valley Expressway (Mohd. Asbi et al. 2007). The failure occurred
immediately after a period of heavy rainfall. The substantial large volume of rock debris (approx.
35,000m3) that came to rest on the expressway blocked the expressway completely and forced the
entire stretch of the expressway to be closed for 6 months for rehabilitation works (Figure 5).
Immediately after the failure, the Highway Concessionaire commissioned site investigations that
included surveys, geological mapping, deep boreholes and laboratory tests to assess the likely
causes of failure and also to provide geotechnical information required to design for
rehabilitation of the failed slope. From the site investigation results, it was inferred that the rock
slope failure was a complex wedge type failure. The wedge was formed by two discontinuities
that daylighted out of the slope and the third discontinuity acted as a release plane. It was also
demonstrated that for the failure to occur there was a requirement for water pressure to be acting
on the potentially unstable wedge. Figure 5 shows the elevation and plan view of the failed rock
slope.
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Figure 5: Rock Slope Failure at Bukit Lanjan, 2003 (newspaper cutting, New Straits Times)
2.4 Debris Flow at KM302 of PLUS North-South Expressway Near Gua Tempurung,
2004
Two lanes for southbound traffic bridge of KM302, North–South Expressway near Gua
Tempurung were closed for three months for rehabilitation works as the result of a debris flow
that occurred on 12 Oct 2004. Tonnes of earth, boulders and trees went crashing down the hill
slope in this incident, as illustrated in Figure 6. Three beams of the bridge were damaged and had
to be replaced. This incident also caused one casualty, public and economic losses and a great
inconvenience to the public.
Figure 6: Debris Flow at KM 302 of PLUS Expressway, 2004
(newspaper cutting, Nanyang Siang Pau)
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2.5 Slope Failure at Putrajaya, 2007
On 22nd March 2007, a massive slope failure occurred at Precinct 9, Putrajaya which twenty-three
vehicles were buried in this landslide and forced about 1,000 residents to vacate their homes at
4.30am. This slope failure involved a 50-metre high hill with a man-made slope about 45 degrees
which was located about 10 metres from the 15-storey apartment. It had been raining heavily in
Putrajaya since the evening of 21 March 2007 till the early morning of 22 March 2007 before the
slope failure happened. Figure 7 shows the collapsed slope with buried vehicles.
Figure 7: Slope Failure at Precinct 9, Putrajaya, 2007
2.6 Collapse of Tourism Complex in Pulau Banding, 2007
Before the collapse of the Tourism Complex at Pulau Banding, Perak on 13th November 2007,
the complex was sitting on a hill slope with its toe near to the edge of the lake, Tasik Temenggor.
The slope extended down into the lake where the water level fluctuates to about 4 meters without
toe protection in the area of fluctuation. The building was completed in 2004. The 15-room
resort was not occupied, as defects such as cracks were found in the buildings. It was reported
that a few months before the failure, a few piles beneath the columns of the building were found
exposed and deflected. On 10th November 2007, part of the building collapsed, followed by a
total collapse of the whole building on 13th November 2007.
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Figure 8: Collapse of Tourism Complex in Pulau Banding, 2007 (The Star, 15 Nov 2007)
3. WHY LANDSLIDES: FACTORS ATTRIBUTED TO LANDSLIDES
A study of the causes of landslides such as design errors, construction errors, design and
construction errors, geological features and maintenance had been carried out by Gue & Tan
(2006) based on 49 investigation cases of primarily large landslides on residual soils. The results
of the study are shown in Table 2.
CAUSES OF
LANDSLIDES NUMBER OF CASES PERCENTAGE (%)
Design Errors 29 60
Construction Errors 4 8
Design and Construction
Errors 10 20
Geological Features 3 6
Maintenance 3 6
Total 49 100
Table 2: Causes of Landslides (after Gue & Tan, 2006)
The results of the study indicate that 60% of the failures are due to inadequacy in design alone.
The inadequacy in design is generally the result of a lack of understanding and appreciation of
the subsoil conditions and geotechnical issues. Failures due to construction errors alone either of
workmanship, materials and/or lack of supervision contributed to 8% of the total cases of
landslides. About 20% of the landslides investigated are caused by a combination of design and
construction errors. For landslides in residual soil slopes, the landslides caused by geological
features only account for 6% which is same as the percentage contributed by a lack of
maintenance.
Before After
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3.1 Geological Features
Landslides due to geological features contributed to about 6% of the total failures investigated.
However, it should be recognised that these geological features, such as discontinuities in
residual soils, especially sedimentary formations, are not usually detectable during the design
stage even with extensive subsurface investigation (boreholes, geophysical methods) by an
experienced engineering geologist or engineer who carries out geological mapping at the site
prior to cutting. Most of these geological features can only be detected after exposing the slopes
during excavation. In view of this, it is best to carry out confirmatory geological slope mapping
of the exposed slopes after excavation, by an experienced engineering geologist or geotechnical
engineer to detect any geological discontinuities that may contribute to potential failure
mechanisms, namely planar sliding, anticline sliding, active-passive wedges, etc. Figures 9 and
10 show the discontinuities found during excavation which were otherwise almost impossible to
detect.
By understanding that geological discontinuities could not be fully addressed during the design
stage, design engineers should make conservative assumptions about the soil/rock parameters and
also the groundwater profile to ensure adequacy in design and should only carry out adjustments
on site after geological slope re-mapping and re-analysis of the slopes. On the contrary, when
optimistic assumptions are made and the results obtained during construction on sites that are less
favourable then expensive options such as retaining walls or slope strengthening using soil nails
are required due to space and boundary constraints. Thus the safety of slopes is often
compromised due to unbudgeted strengthening and additional protection works being needed.
Figure 9: Block Failure of Sedimentary Formation (After Liew S.S. 2005)
- 10 -
Figure 10: Inconsistent Weathering Profile (After Liew S.S. 2005)
3.2 Design and Construction Errors
The majority of these failures investigated by Gue & Tan (2006) were avoidable if extra care was
taken and input from engineers with relevant experience in geotechnical engineering was sought
from planning to construction. Many of the landslides which were caused by design errors
reported above were due to the following:-
1) The abuse of the prescriptive method on the slope for cut or fill slopes without proper
geotechnical analyses and assessment. It is very common in Malaysia to find many cut
slopes formed for residual soils that are 1V:1H (which means one vertical: one horizontal =
45 degrees angle). Based on literature published on residual soils and the authors’ own
experience of residual soils, it is not likely, or impossible, for residual soils to have the
effective parameters (c’, φ’) to maintain the stability of the slopes even without water table
and geological features unless it is not a soil slope but a rock slope. The authors’ own
experiences indicates that the φ’ values of residual soils generally ranges from 29o to 36o and
mainly depend on the particle size distribution of the materials. Therefore, if proper analysis
of the slopes’ stability was carried out with correct soil parameters, most of these 45o gradient
slopes would not have a sufficient Factor of Safety (FOS) recommended against slip failure
in the long term, even with some effective cohesion. In summary, engineers should not only
follow the slope gradients (e.g. 1V: 1H) that have been done previously, without proper
geotechnical analysis and design.
2) Subsurface investigation (S.I.) and laboratory tests were not carried out to obtain
representative soil parameters, subsoil and groundwater profiles for design and analysis of
slopes. Therefore, the analysis and design carried out are not representative of the actual site
conditions, and are thus unsafe.
3) A lack of good understanding of fundamental soil mechanics, so that the most critical
condition of cut slopes is in the long term (in the “Drained Condition”). Therefore, it is
necessary to adopt effective shear strength parameters for the “Drained Analysis” of the cut
slopes in residual soils instead of undrained shear strength (su or cu).
For landslides that were caused by construction errors alone or combined with design, the
common construction errors are as follows:-
- 11 -
1) Tipping or dumping of loose fill down the slopes to form a filled platform or filled slope.
This is the most rampant construction error for earthworks construction in Malaysia.
Contractors carrying out the filling works on slopes will find it most “convenient” and “easy”
to dump or tip soil down the slopes to form the fill. The condition is worsened by not
removing the vegetation on the slopes, causing the bio-degradable materials to be trapped
beneath the dumped fill, forming a potential slip plane with the bio-degradable materials
(vegetation). The uncompacted fill slopes, having a very low Factor of Safety, will likely fail
in the long term.
2) Errors in the construction method, such as forming cut slopes by excavating slopes from the
bottom (undermining) instead of the correct practice of cutting from the top downwards. This
wrong practice will trigger landslides or induce potential shear planes extending beyond the
proposed cut slope profile.
3) Over-excavation of cut slopes. Contractors unintentionally over-excavate cut slopes and then
try to fill back the excavated materials to reform the slope to the required gradient. The
uncompacted loose materials will eventually slip down.
The way to prevent these bad construction practices is to have proper full-time supervision by
members of the design consultant together with reliable and responsible earthwork contractors
having clear approved method statements for construction. Failure of slopes and retaining walls
can also take place if the temporary works (e.g. temporary excavation) are not properly designed
and constructed.
3.3 Maintenance
Poorly maintained slopes can lead to slope failure. These may include amongst others,
damaged/cracked drains, inadequate surface erosion control and clogged drains. The common
problems of landslides caused by a lack of maintenance are blockage of drains for surface runoff,
and erosion. Blockage of drains will cause large volumes of water to gush down a slope
causing erosion to the slope and the formation of gullies. These gullies will further deteriorate
into big scars on the slopes and will finally lead to landslides.
Figure 11 shows the formation of rills and gullies and Figure 12 shows localized landslips caused
by erosion which will propagate with time into landslides if erosion control is ignored. If proper
maintenance is carried out, then all these small defects would have been rectified and landslides
caused by erosion would be prevented.

4. GOOD DESIGN AND CONSTRUCTION PRACTICES FOR SLOPE ENGINEERING
4.1 Planning, Analysis and Design of Slopes
Desk Study
Desk study includes reviewing of geological maps, memoirs, topographic maps and aerial
photographs of the site and adjacent areas so that the engineers are aware of the geology of the
site, geomorphology features, previous and present land use, current development, construction
activities, problem areas like previous slope failure, etc.
Site Reconnaissance
Site reconnaissance is required to confirm the information acquired from the desk study and also
to obtain additional information from the site. For hillsite development, it is also very important
to locate and study the landslip features to identify previous landslides or collapses that can act as
indicators of the stability of the existing slopes.
Subsurface Investigation
Subsurface investigation (SI) should be properly planned to obtain representative subsurface
condition of the whole slope such as general depth of soft soil, hard stratum, depth of bedrock,
geological weak zones, clay seams or layers, and the groundwater regime. The planning of
exploratory boreholes should take into consideration the slope profile instead of following a
general grid pattern. A minimum of three (3) boreholes per cross-section (one on slope crest, one
at mid-slope and one at slope toe) is recommended so as to obtain representative subsurface
conditions of the whole slope.
Analysis and Design of slopes
For the design of the slopes, correct information on soil properties, the groundwater regime, the
geology of the site, selection and methodology for analysis are important factors that require the
special attention of the design engineer. A detailed analysis of soil slopes can be found in Tan &
Chow (2004) and Gue & Tan (2000).
For the selection of Factor of Safety (FOS) against a slope failure, the recommendation by
Geotechnical Manual for Slopes (GCO, 1991) of Hong Kong with minor modifications to suit
local conditions is normally selected with consideration of two main factors, namely, Risk-to-life
or Consequence to life (e.g. casualties) and Economic Risk or Consequence (e.g. damage to
property or services). Further details on selection of FOS can be found in Gue & Tan (2004).
Design of Cut and Fill Slopes
The vertical interval of slopes between intermediate berm is usually about 5m to 6m in Malaysia.
GCO (1991) recommends that the vertical interval of slopes should not be more than 7.5m. The
berms must be at least 1.5m wide for easy maintenance. The purpose of berms with drains is to
reduce the volume and velocity of runoff on the slope surface and the consequent reduction of
erosion potential and infiltration. The adopted slope gradient should depend on the results of
analysis and design based on moderately conservative strength parameters and representative
groundwater levels.
For fill slopes before the placing of fill, the vegetation, topsoil and any other unsuitable material
should be properly removed. The foundation should also be benched to key the fill into an
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existing slope. A free-draining layer conforming to the filter criteria is normally required
between the fill and natural ground to eliminate the possibility of high pore pressures from
developing and causing slope instability, especially when there is an existing surface or
intermittent streams and depressions. Sufficient numbers of discharge drains should be placed to
collect the water in the filter layer and discharge it outside the limits of the fill and away from the
slopes.
Surface Protection and Drainage
Surface drainage and protection are necessary to maintain the stability of the designed slopes
through reduction of infiltration and erosion caused by heavy rain, especially during monsoon
seasons. Runoffs from both the slopes and the catchment areas upslope should be effectively cut
off, collected and led to convenient points of discharge away from the slopes. Details on surface
protection and drainage can be found in Gue & Tan (2004).
Catchment Study
Catchment study is rarely carried out for the provision of surface drainage capacity to carry the
runoffs in current slope engineering practice. Under-provision of surface and subsurface
drainages can lead to infiltration and spillage of the surface runoffs to the slopes, cause saturation
of slopes, surface erosions to the slopes and can result in slope deterioration with time.
Fill Slopes Over Depressions or Valleys
Depressions or valleys are the preferred water path of natural surface runoffs. Streams or
intermittent streams are usually formed at these depressions and valleys, especially during heavy
rain. In the meantime, intermittent streams at depressions or valleys will also transport sediments
from upstream and deposit these sediments at the depression or valley and form a layer of soft or
loose material and debris.
For slopes which are formed by filling over a depression or valley, the possibility of having
saturation of slopes and developing slip planes through the pre-existence of weak soft or loose
layers with debris is high.
Therefore, extra care should be exercised on the fill slopes over depressions or valleys by
adopting the following measures to mitigate occurrence of slope failure: -
1) To provide adequate surface drainage by calculating the capacity required based on
catchment study to reduce infiltration of surface runoffs to the slopes.
2) Subsurface drainages should be adequately provided to drain out water from a slope to
avoid saturation of the slope and rising of the groundwater level. Increases in ground
water levels will reduce the FOS of the slope.
3) To replace shallow weak materials by compacted good fill material during the filling
works to enhance the slope stability FOS.
Slopes Next to Water Courses
For slopes next to water courses such as river bank slopes, beaches, pond side slopes, etc, the
slope should be robustly designed by considering the probable critical conditions such as
saturated slope with rapid drawn-down conditions, scouring of slope toe due to flow and wave
actions, etc. Properly designed riprap or other protection measures are needed over the tidal
range.
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4.2 Construction Controls
Supervision and Coordination
The supervising personnel should have sufficient knowledge and experience in geotechnical
engineering to identify any irregularities of the subsurface conditions (e.g. soil types, surface
drainage, groundwater, weak planes such as clay seams etc.) that might be different from those
envisaged and adopted in the design. Close coordination and communication between design
engineer(s) in the office and supervising engineer(s) are necessary so that modification of the
design to suit the change of site conditions could be carried out when needed. This should be
carried out effectively during construction to prevent failure and un-necessary remedial works
during the service life of the project. Site staff should keep detailed records of the progress and
the conditions encountered when carrying out the work in particular if irregularities like clay
seams, significant seepage of groundwater are observed. Sufficient photographs of the site
before, during and after construction should be taken. These photographs should be supplemented
by information such as dates, weather conditions or irregularities of the subsoil conditions
observed during excavation.
Filling of Slopes
Whenever possible, construction programmes should be arranged such that fill is placed during
the dry season, when the moisture content of the fill can be controlled more easily. When filling,
tipping should not be allowed and all fill should be placed in layers not exceeding 300mm to
450mm thick depending on the type of compacting plant used (unless compaction trails proved
that thicker loose thickness is achievable) in loose form per layer and uniformly compacted in
near-horizontal layers to achieve the required degree of compaction before the next layer is
applied. The degree of compaction for fill to be placed on slopes is usually at least 90% to 95%
of British Standard maximum dry density (Standard Proctor) depending on the height of the slope
and the strength required.
Cutting of Slopes
Cutting of slopes is usually carried out from top-down followed by works like drains and turfing.
When carrying out excavation of the cut slopes, care must be taken to avoid overcutting and
loosening of the finished surface which may lead to severe surface erosion. Minor trimming
should be carried out either with light machinery or by hand as appropriate. It is also a good
practice to construct first the interceptor drains or berm drains with proper permanent or
temporary outlets and suitable dissipators before bulk excavation is carried out or before
continuing to excavate the next bench.
Surface Protection of Slopes
For all exposed slopes, slope protection such as turfing or hydroseeding should be carried out
within a short period (not more than 14 days and 7 days during the dry and wet seasons
respectively) after the bulk excavation or filling for each berm. All cut slopes should be graded
to form suitable horizontal groves (not vertical groves) using suitable motor graders before
hydroseeding. This is to prevent gullies from forming on the cut slopes by running water before
the full growth of the vegetation, and also to enhance the growth of vegetation.
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4.3 Maintenance of Slopes
Guideline for Slope Maintenance
A good guideline from GEO of Hong Kong such as “Geoguide 5 – Guide to Slope Maintenance”
(2003) for engineers and the “Layman’s Guide to Slope Maintenance” which is suitable for the
laymen should be referred to.
Geoguide-5 (2003) recommends maintenance inspections be sub-divided into three categories:
(A) Routine Maintenance Inspections, which can be carried out adequately by any responsible
person with no professional geotechnical knowledge (layman).
(B) Engineer Inspections for Maintenance, which should be carried out by a professionallyqualified
and experienced geotechnical engineer.
(C) Regular Monitoring of Special Measures, which should be carried out by a firm with
special expertise in the particular type of monitoring service required. Such monitoring is
only necessary where the long term stability of the slope or retaining wall relies on
specific measures which are liable to become less effective or deteriorate with time.
Frequency of Maintenance Inspections
Since Malaysia has at least two monsoon seasons, Routine Maintenance Inspections (RTI) by a
layman should be carried out a minimum of twice a year for slopes with negligible or low risk-tolife.
For slopes with high risk-to-life, more frequent RTI is required (once a month). In addition,
it is good practice to inspect all the drainage channels to clear any blockage by siltation or
vegetation growth and repair all cracked drains before the monsoon. Inspection should also be
carried out after every heavy rainstorm.
Category B Engineer Inspections for Maintenance, should be taken to prevent slope failure when
the Routine Maintenance Inspection by laymen observed something unusual or abnormal, such as
the occurrence of cracks, settling ground, bulging or distorting of walls or settlement of the crest
platform. Geoguide-5 (2003) recommends as an absolute minimum that an Engineer Inspection
for Maintenance should be conducted once every five years or more as requested by those who
carry out the Routine Maintenance Inspections. More frequent inspections may be desirable for
slopes and retaining walls in the high risk-to-life category.
5. SUGGESTIONS FOR IMPROVEMENT OF THE ENGINEERING AND
MANAGEMENT OF SLOPES
5.1 Practitioners and Professionals in Slope Engineering
The institution of Engineers, Malaysia (IEM), under its own initiative, formed a taskforce in 1999
to formulate policies and procedures for mitigating the risk of landslides in hilly terrain
developments. IEM (2000) produced a report entitled, “The policies and procedures for
mitigating the risk of landslide on hill-site development” with the aim of providing uniform,
consistent, and effective policies and procedures for consideration and implementation by the
Government of Malaysia. However, the recommendations by IEM were not immediately
accepted and acted on by the Government (C.H. Abdullah et al. 2007).
Practitioners and professionals that involve in slope engineering works should practice ethically
and professionally and should only practice in the area of their expertise to ensure the safety of
the design and to mitigate the risk of landslides.
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Stakeholders such as engineering universities and colleges, the Association of Consulting
Engineers Malaysia (ACEM) and the IEM should work together to develop a series of structured
training modules on slope engineering so as to inculcate better understanding of the practitioners
so that the public could benefit.
Apart from having structured training modules, all practitioners should also think another step
ahead on how to further improve the current slope engineering practices through Research and
Development (R&D) to enhance safety, speed of construction and economical aspects. It is
important to equip practitioners with R&D skills to improve construction industry’s
competitiveness and to prepare ourselves for globalisation.
A successful example by Hong Kong Geotechnical Engineering Office (GEO) on suggesting a
new cost-effective and eco-friendly method of natural slope stabilisation through R&D
(Campbell et al. 2005) is discussed in the following section.
In 2003, the Hong Kong GEO completed a planting trial involving the use of native small tree
and shrub species on steep slopes. Based on this, guidelines were promulgated on the selection of
suitable vegetation species for man-made slopes. Trials were also initiated on repairing natural
terrain landslide scars by means of predominantly native vegetation species (Figure 13). The
interim findings are documented by Campbell et al. (2005).
(a) Landslide scar prior to (left) and during (right) installation of bioengineering measures
(b) Landslide scar during (left) and after (right) installation of bioengineering measures
Figure 13: Use of Bioengineering Measures for Repair of Natural Terrain Landslides
(after Wong & Ho 2006)
- 17 -
5.2 Slope Management in the Public Sector (Abdullah et al. 2007)
The first to document on guidelines in hilly areas development was the Urban and Rural Planning
Department in 1997. The guidelines addressed the issues of planning and development in
highlands, on slopes, natural waterways, and water catchment areas. In June 2002, the Geology
and Minerals Department of Malaysia produced guidelines on hillsite development. The
guidelines considered the angle of the natural slopes and geology of the area. The areas were then
classified into 4 categories which were termed as Class l, ll, lll and lV. Class l is the least severe
in terms of terrain grading whereby slope angles are less than 15o. Class lV was the highest risk,
where, absolutely no development will be allowed in this area.
Also in June 2002, the National Disaster Management Committee in the Prime Minister’s
Department directed Jabatan Kerja Raya (JKR) to form a Working Group on Landslide Study
with the objectives of identifying areas with high landslide risks and coming up with mitigative
measures. The Working Group was officially inaugurated on August 14, 2002 and subsequently 4
subcommittees were formed, namely (Abdullah et al. 2007):
• Sub-committee for Forensic Investigation of landslides
• Sub-committee for Disaster Management during landslides
• Sub-committee for Co-ordination and Information Sharing
• Sub-committee for Research Coordination.
The first task given to the committee was to investigate the Taman Hillview landslide that killed
eight (8) people at the end of 2002. The overall mandate given to JKR during this time was not
very successfully implemented because the Slope Engineering Unit was then placed under the
Road Maintenance Division, where it had to compete for attention and resources within the
division.
The Slope Engineering Branch (CKC) was established as a branch within the JKR in February
2004 with the aim of managing and monitoring of slopes throughout the country. CKC has 6
units that deal with slope matters. They are the Slope Safety Unit that coordinates and controls
the budget for the slope repair works; the Slope Management Unit that collects spatial and non
spatial data and produce hazard maps for slopes; the IT and Documentation Unit whose job is to
archive and disseminate slope data and information through the website and by archiving; the
Research and Development Unit whose function includes research, initiating cooperation with
universities (local and abroad) and conducting National Slope Master Plan studies; the Forensic
Unit,responsible for landslide investigation and preparing standards and guidelines for slope
design, and finally the Quality, Training and Public Awareness Unit is responsible for training
personnel in JKR and creating public awareness (Abdullah et al. 2007).
Apart from the above, there are also numerous guidelines and regulations available from the
following government authorities and associations related to slope management: -
a) Department of Environment (DOE)
b) Geology and Mineral Department (JMG)
c) Majlis Perbandaran Ampang Jaya and other local authorities such as Penang Local Council
etc.
d) Ministry of Housing and Local Governments (MHLG)
e) Urban and Rural Planning Department (JPBD)
f) The Institution of Engineers Malaysia (IEM)
- 18 -
Some of these guidelines and regulations are unclear and do not add value to safety, enhance
slope stability and protection, environmental friendliness and sustainability of the slope
engineering projects. These guidelines and regulations should be harmonized and improved
further by developing unified guidelines for good practices in the planning, design, construction,
supervision, maintenance and monitoring of slope engineering projects, as well as ensuring the
safety, environmental friendliness and sustainability of these projects.
5.3 National Slope Master Plan (NSMP)
In view of the slope failure occurrences in recent years, the Malaysian Government instructed
JKR to carry out the NSMP study in May 2004 to be completed by March 2008. The goal of this
study is to provide detailed elements of a comprehensive and effective national policy, strategy
and action plan for reducing losses from landslides on slopes nationwide including activities at
the national, state and local levels, in both the public and private sectors (Abdullah et al. 2007).
The NSMP consisted of 10 key objectives which were translated into 10 components of the
study. The components of the NSMP and the summary of their objectives are as follows:
ii. Policies and institutional framework - improve policies and institutional frameworks
iii. Hazard mapping and assessments – develop a plan for mapping and assessing landslide
hazards and also develop standards and guidelines for landslide hazard mapping
iv. Early warning and real-time monitoring system- to develop a national landslide hazard
monitoring, prediction and early warning system
v. Loss assessment – assess the current data on landslide losses and develop a national plan for
compilation, maintenance and evaluation of data from landslides
vi. Information collection, interpretation, dissemination, and archiving – evaluate the state-ofthe-
art technologies and methodologies for the dissemination and archiving of technical
information
vii. Training - develop training programs for personnel involved in landslides
viii. Public awareness and education – evaluate and develop education programs related to the
predictive understanding of landslides
ix. Loss reduction measures – evaluate and develop effective planning, design, construction and
maintenance with a view to landslide hazard reduction
x. Emergency preparedness, response and recovery – develop a national plan for a coordinated
landslide rapid response capability.
xi. Research and development - develop a predictive understanding of landslide processes,
thresholds and triggering mechanisms
The NSMP is to be implemented in 3 phases: the first phase is called the short term which would
cover the first 5 years; the second phase is known as the medium term i.e. the period of
implementation between 5 and 10 years; and final phase is known as the long term, which is the
period of implementation of 10 to 15 years and beyond.
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5.4 Undergraduates in Slope Engineering
Apart from improving the understanding of practitioners and policy implementation by the
government on slope engineering and management, emphasis should also be given to how to
improve undergraduates’ understanding on slope engineering fundamentals, which is currently
lacking, and this is one of the most important components to improve slope engineering.
Consequently, universities and colleges should review and update the undergraduate syllabus
from time to time with the assistance of active experienced practitioners to ensure graduates
possess enough fundamentals to suit industry needs.
Besides, structured modules of lecture notes on slope engineering and management should be
developed and updated regularly by pooling resources from a group of universities, colleges and
passionate practitioners to ease the workload of the lecturers so that the quality of the lecture
notes is assured.
Lecturers should also obtain more exposure on slope engineering with the help of practitioners
and getting them to give lectures related to mitigation and prevention of slope failures.
6. CONCLUSION
This keynote presents a brief review on six major landslides in Malaysia that includes old and
new slope failures. Most of the landslides were induced by high rainfall and 80% of the
landslides were caused by man-made factors (design errors and construction errors). Some good
design and construction practices were put forward for slope engineering on planning, analysis
and design aspects, construction control aspects and slope maintenance aspects. Finally, this
keynote also discussed some suggestions on improvement for practitioners, undergraduates,
public sector and implementation of government policy. Practitioners should be equipped with
R&D skills to improve construction industry’s competitiveness and be prepared for globalisation.

AIR POLLUTION

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                             In many people’s mind air pollution is associated with contamination of urban air from automobiles exhaust and industrial influents. But every year  the indoor air pollution is responsible for the death of 1.6million people ,that is a death in every 20 second .Exposure is high among women and children who spend  most of their time near the domestic hearth .
             The  severity  of indoor air pollution is aggravated by the fact that the more than half  world’s house wife  cook their  food on unprocessed  solid fuels , buildings are built more air tightly to save money spent on heating and cooling .At the same time people are using more and more irritating products such as hair spray , other cleaning detergents pesticides and other which are harmful to health.
Indoor air pollution is the presence of one or more contaminants indoors that
carry a certain degree of human health risk. Indoor air issues may be traced to the beginning of civilization. Prehistoric records note the problem of smoke in caves. However, over the last three decades the public has become more aware of indoor air pollution. Various studies show that people spend 65 to 90 percent of their time indoors; 65 percent of that time is spent at home. Field studies of human exposure to air pollutants indicate that indoor air levels of many pollutants may be two to five times, and on occasion more than one hundred times, higher than outdoor levels.



2.INDOOR AIR POLLUTION
           Indoor air pollution is the presence of one or more contaminants indoors that carry a certain degree of human health risk. Indoor air issues may be traced to the beginning of civilization. Prehistoric records note the problem of smoke in caves. However, over the last three decades the public has become more aware of indoor air pollution. Various studies show that people spend 65 to 90 percent of their time indoors; 65 percent of that time is spent at home. Field studies of human exposure to air pollutants indicate that indoor air levels of many pollutants may be two to five times, and on occasion more than one hundred times, higher than outdoor levels.
   2.1. INDOOR AIR QUALITY  (  I.A.Q )
          It is the term refering to the air quality within and around buildings and structures , it is related to the health and comfort of the building occupants.IAQ can be effected by microorganisms,gas,particulates or any mass or energy stressor that can induce adverse health conditions.Indoor air is becoming an increasingly more concerning health hazards than outdoor air.(1)

3.COMMON POLLUTANTS

The four principle sources of pollutants of indoor air.
                 1.Combustion.
                 2.Building materials.
     3.The ground under the building.
     4.Biaerosols.
            In the developed countries the most important indoor air pollutants are thecompustion products.Radon,asbetos ,volatile organic compound , pesticides , heavy metals animal danfe mits , moulds and environmental tobacco smoke.
            In developing countries the pollutants are combustion productos of unprocessed solid biomass fuel used by the poor urban and rural folk for cooking and heating .A recent report of WHO states the “Rule of thousands”.Which states that a pollutant released in indoor is thousand times more likely to reach peoples lung than a pollutant released outside.

3.1 Radon
           It is a invisible , radioactive  atomic gas that result from radioactive decay of radium ,which may be found in the formation beneath buildings .It will tend to accumulate at the floor level.These deposits in the lung of the occupants either directly or by ataching to air born particles , which are then inhaled . To dilute the way that they occur from nature deacay , ventilation is provided.

3.2  Molds and Allergens
            These biological chemicalscan arrise from a host of means , but there are two common classes
·         moisture induced growth of mold colonies
·         natural substances released from animal clander
            Moisture buid inside the home may arise from the water penetrating compromised area of the building envelops and the skin , plumbing laeks , from condensation due to improper ventilation  or from the ground moisture penetrating into the building parts.In the area where the cellulosic material fail to dry witin 48 hours , mold mildew can propagate  and release allergenic spores into the air .Indoor  mold growth can be inhabited by keeping humidity level below 50% and eliminating any water leak.

3.3  Carbon monoxide
            A clourless , odourless , gas that is a by product of incomplect compustion of fossile fuels . Common source of carbon monoxide  are tubacco smoke,space heaters using fossile fuels ,defective central heating furnances and automobiles exhaust .Indoor carbon monoxide levels may rise aout 25-35 ppm.(4)Current ventilation standard recognise that significantly more air flow is needed in smoking areas than in the non-smoking area .This need is based primarly on achieving acceptable odour level than controlling carbon doixide level.

3.4  Volatile organic compound (V.O.C)
            It is emitted as gas from the certain solid or voc are emmited by a wide array of products such as paints , varnish , pesticdes , building materials and furnishing , office equipments such as copier , printer correction fluid , carbonless copypaper,graphics and craft materials including gluye ,permenent marker , photographic solutions.Testing emmision from building materials used indoor has been increasing commenly for floor level , paint.

3.5  Legionella
             It is a water born bacterium that grow best in slow moving or silt water.The primary route of exposure is aerosolation ,most commenly from evaporative cooling or showerhead .      It is mostly found in commercial building is from poorly placed or maintained evaporative cooling tower , which often release aerosolzed water that may enter near by ventilation  intake .Outbreak in medical facilities and nursing homes where patients are immuno-supressed . The reason is legionella .Prevention measures include adjusting normal hot water level to allow far for 120 degreeF at the tap , evaluating facility design lay out , removing favect aerators and preiodic testing in suspect area.
3.6   Asbetos Fiber
            Asbetos is found in older homes and buildings , but it is most dangerious in school and industrial setting .It is once widely used in shingles , fire proofing ,heating system , floor and ceiling tiles in the older buildings . when they damage it is dispersed into the air .The removal of the asbestos containg material is not always wise because these fiber can release harmful substance into the air during the removal process . The symptom of this disease does not occur for 20-30 years after the first exposure.A management programme for intact asbetos –containing material is often recommended instead.

3.7    Carbon di oxide
            It is a surrogate for the indoor pollution emitted by the human beings.If co2 level is high it causes the occupant to grow drowsy , get head aches , or function at lower level .Indoor leles are the indicator of  the adqacy of outdoor air ventilation raelative to indoor occupant desity.This total co2 should be reduced to a differenc eof less tha 600ppm above the outdoor level.


3.8   Formaldehyde
It is a component in the urea formaldehyde which is used as building material for insulation It is used as plywood , adhesive , a binder in particle board and a component  in flor covering , fabrics .It may also causes cancer.

3.9   Respirable Particular Matter (R.P.M)
The is another board category of indoor pollutants that including particles such as dust and pollens and aerosols in the size range thet can reach the lunga when inhaled.High RPM can cause eye and respiractory tract irritation.For many people the main exposure to RPM is from tobacco smoke .Smokers receive a higher close than non smokers.And smoking can cause an increase factor of 3-40 in RPM over back ground level.If the sources of RPM is confined to relatively small area , air cleaner can be used . Limitataion  on smoking may be a solution when tobacco is amajor source of RPM.

3.10   Pesticides
            Pesticides in home or office can irritate eye , nose and throat and may damage the central nervous system or may lead to an increasd risk of cancer . Some pesticides such as chlorade , dieidrin used to kill terminate have been banned and their indoor use restricited because they remain for such a long period.

3.11  Role of Humidity
·         Low humidity can cause particles and vapours in air to be more irritating at high levels.
·         High humidity aggrevates odour problems and favour mold growth .It lead tocomplaint of stuffines and thermal discomfort.


    Table 3.1: Pollutants and max concentration

Pollutant

Max Concentration
Living area

Max Concentration
Work place

Carbon dioxide (CO2)

0.1%

0.5%

Carbon monoxide (CO)

3 mg/m³

30 mg/m³

Sulphurous gases

0.5 mg/m³

20 mg/m³



Table 3.2: Types of fuel used and their concentration in different areas

Type of fuel

CO concentrations (ppm)
Kitchen

CO concentrations (ppm)
Bedroom

CO concentrations (ppm)
Outdoor

Coal briquettes





5

4

2


26

19

2

Wood





17

16

2


30

31

2


4. SOME DISEASES ASSOCIATED  WITH INDOOR AIR POLLUTION

Indoor air pollution has been associated with a wide range of health outcomes, and the evidence for these associations has been classified as strong, moderate or tentative in a recent systematic review. Included in the above assessment were only those health outcomes for which the evidence for indoor air pollution as a cause was classified as strong. There is consistent evidence that exposure to indoor air pollution increases the risk of pneumonia among children under five years, and chronic respiratory disease and lung cancer (in relation to coal use) among adults over 30 years old. The evidence for a link with lung cancer from exposure to biomass smoke, and for a link with asthma, cataracts and tuberculosis was considered moderate. On the basis of the limited available studies, there is tentative evidence for an association between indoor air pollution and adverse pregnancy outcomes, in particular low birth weight, or ischaemic heart disease and nasopharyngeal and laryngeal cancers.

4.1   Respiratory Diseases
The effect of air pollution generally would depend on the consumption of the air that is inhaled which will depend on the inhaled which will depend on the inhilation occur .It is most common in women and children.
4.2   Chloric Pulmonary Disease
In India only 75% of the men and 10% of the women are smokers .But the chronic pulmonary disease is more common in young women.
4.3   Pneumonia
It is the disease of industrial workers occuptionally exposed to fine minerals dust particles over a long time.It is the single most important cause of death in children under  five year. More than 900000 of the 2million annual death due to pneumonia. 
4.4   Lung cancer
Smoking is the major cause of lung cancer .The tuberculosis which is common in Indian women it is a risk factor of developing lung cancer in indian non smoking ,it may be concluded that at the present there is no evidance for biomass fuel.(2)

4.5   Catract

During cooking paticularly with biomass fuel ,air has to be blown into the fire from time to time , especially when the fuel is moist and fire is smouldering. This causes considerable exposure of eye to the emanating smoke .The growing evidence that the environmental tobacco smoke causes cataract.

4.6 Adverse Preganancy Effect

            Low birth rate is an important public health problem in the developing countries attributed mainly to under nutrition in the pregnant women.It causes serious consequences including increased possibility of death during the infancy.Exposure to the carbon monoxide from tobacco smoke during the pregnancy has been associated with LBW.
            While precise mechanism of how that small particles causes disease is still unclean , it is known that small particles and several of pollutants contained indoor causes harmful diseases.


Table 4.1
 Health Symptoms Associat With Different Environmental Condition


Environmental Condition(s)
Symptoms
• Ergonomic Conditions
• Headache
• Noise and Vibration
• Fatigue
• Poor Concentration
• Dizziness
• Tiredness
• Headache with nausea
• Ringing in ears
• Pounding heart
• Relative Humidity
• Dry throat
• Shortness of breath or bronchial asthma
• Irritation and infection of respiratory tract
• Relative Humidity
• Nasal problems (stuffiness, irritation)
• High Temperatures
• Warm Air
• Skin problems (dryness, irritation, rashes)
• Low Relative Humidity
• Excessive Air Movement
• Artificial Light
• Eye problems (burning, dry gritty eye)

5.PRECAUTION MEASURES


·         The air pollution control regulation should have provision for compulsory  testing of products at the point of manufacture to assure that they will not pollute indoor air.

·         Architect and Engineer should make sure that air flow is not reduced to a danger point inn the guest for energy efficiency.


·         Cautionary label should be attaached to the construction material that contain formaldehyde resin.

·         Muncipal health authorities should be authorised to test air within the homes when a physical suspect .Presence of any harmful pollutants might be damaging the residents health.


·         Switching to cleaner alternatives such as gas , electricity  or solsr energy

·         Improve stove or hoods that vent health damageing pollutants to the outside.

Table 5.1 Major indoor air pollutants, sources,health effects and control 
Pollutants
Sources
Health Effects
What to do?
By-products of combustion (such as CO, CO2, NOx)
Unvented kerosene and gas heaters, gas appliances, wood- and gas-burning fireplaces, leaking chimneys and furnaces, tobacco smoke, automobile exhaust in attached garages
Eye, nose, and throat irritation, impaired lung function and respiratory function in children, bronchitis, lung cancer, flu-like symptoms.
1. Avoid use of unvented gas or kerosene space heaters
2. Keep gas appliances and furnaces properly adjusted
3. Install and use exhaust fans
4. Change filters on heating/cooling systems and air cleaners
5. Increase of supply of outside air
6. Proper location of air intakes to avoid exhaust from vehicles
Environmental tobacco smoke
Cigarettes, cigars, pipes
Eye, nose, and throat irritation, headaches, pneumonia. Increased risk of respiratory and ear infections in children. Lung cancer and increased risk of heart disease.
1. Stop smoking
2. Discourage others from smoking
3. Isolate smokers outdoors
Formaldehyde
Pressed wood products (hardwood, plywood wall paneling, particleboard, fiberboard) used in buildings and furniture, urea-formaldehyde foam insulation, permanent press textiles, glue, ETS, vehicle exhaust, stoves, fireplaces
Eye, nose, and throat irritation, coughing, fatigue, rashes, and allergic reactions. Causes cancer in animals. Death at very high concentration.
1. Use products with lower emission rates of formaldehyde
2. Keep humidity low in house
3. Increase ventilation
4. Aging or baking of products
Other volatile organic compounds
Paints, solvents, wood preservatives, aerosol sprays, cleaners and disinfectants, moth repellents, air fresheners, hobby supplies, and dry cleaned clothes
Eye, nose, and throat irritation, headaches, loss of coordination; nausea, damage to kidney and central nervous system. Some cause cancer in animals. Some may cause cancer in humans.
1. Buy only what you need
2. Read labels and follow instructions
3. Use in well-ventilated areas or outdoors
4. Hang dry cleaned clothes in an open area for about 6 hours.
Radon
Local geology, soil, water
Lung cancer, possibility of stomach cancer
1. Seal cracks and openings in the basement
2. Ventilate crawl space
3. Subslab suction
4. Increase ventilation
Pesticides
Garden and lawn chemicals, poisons for pest control
Eye, nose, and throat irritation, damage to central nervous system and kidney, cancer
1. Use nonchemicals if possible
2. Avoid storage in the house
3. Follow manufacturer's instructions
4. Increase ventilation
Asbestos
Deteriorating or damaged insulation, fireproofing, or acoustical materials
Cancer and lung diseases (smokers at higher risk)
1. Test the suspected material
2. Remove asbestos by a trained contractor or develop a maintenance plan
3. Encapsulation of material containing asbestos
Heavy metals
Paints, automobiles, tobacco smoke, soil, and dust
Headaches, irritation in mouth, rash, excessive perspiration, kidney damage
1. Vacuum regularly
2. Removal of lead based paint
Bioaerosols
Humans, pets, moist surfaces, humidifiers, ventilation systems, drip pans, cooling coils in air handling units, plants, outside air
Legionnaires' disease, humidifier fever, influenza
1. Remove the source
2. Maintenance of equipment
3. Humidity control to 40% to 60%
4. Use of filters in ventilation
5. Air cleaning by the use of disinfectants
SOURCE: Adapted from U.S. Environmental Protection Agency and Consumer Product Safety Commission.



6.INTERVENTION

Adequate evidence exists to indicate that indoor air pollution in India is responsible for a high degree of morbidity and mortality warranting immediate steps forintervention. The intervention programme should include
(i)                  Public awareness;
(ii)                Change in pattern of fuel use;
(iii)               Modification in stove design;
(iv)               Improvement in the ventilation; and
(v)                 Multisectoral approach.

6.1 Public Awareness
The first and the most important step in the prevention of illnesses resulting from biomass fuels is to educate the public, administrators and politicians to ensure their commitment and promoting awareness of the long-term health effects on the part of users. This may lead to people finding ways of minimizing exposure through better kitchen management and infant protection.Change in Pattern of Fuel UseThe choice of fuel is mainly a matter of availability,affordability and habit. The gobar gas plant which uses biomass mainly dung has been successfully demonstrated to produce economically viable quantities of cooking gas and manure. Recently, the Government of Andhra Pradesh has introduced a programme called the Deepam Scheme to subsidize the cylinder deposit fee for women from households with incomes below the poverty line tofacilitate the switch from biomass to LPG. Such schemes will encourage the rural poor to use cleaner fuels. Theuse of solar energy for cooking is also recommended.

6.2  Modification in Stove Design
Use of cleaner fuels should be the long-term goal for the intervention. Till this goal is achieved, efforts should be made to modify the stoves to make them fuel efficient and provide them with a mechanism (eg chimney) to remove pollutants from the indoor environment. Several designs of such stoves have been produced. NIOH study showed significant decrease in levels of SPM, SO2, Nox and formaldehyde with specially designed smokeless stoves in comparison with traditional cooking stoves. However, they have not been accepted widely. Large scale acceptance of improved stoves would require determined efforts. The most important barriers to new stove introduction are not technical but social.(3)

6.3 Improvement in Ventilation
In many parts of the country poor rural folk are provided with subsidized houses under various government/international agencies aided schemes.Ventilation in the kitchen should be given due priority in the design of the houses. In existing houses, measures such as putting a window above the cooking stove and providing cross ventilation through the door may help in diluting the pollution load.

6.4 Multisectoral Approach
Effective tackling of indoor air pollution requires collaboration and commitment between agencies responsible for health, energy, environment, housing and rural development.



7.THE STRATEGY OF CONTROLLING INDOOR AIR QUALITY THROUGH THE WHOLE ACTUALIZATION COURSE OF SUSTAINABLE BUILDING
How to create a good indoor air quality has become the key issue in the indoor environment of sustainable building. The main factors that affect the indoor air quality include: pollution of outdoor air, building materials and decoration materials, fresh air quantity, mildew, particle and other pollutants caused by the air-conditioning system, air current form of single area and multil-area, office equipment, furniture, electrical appliance, indoor fuel and cooking oil, the domestic chemicals, smoking, staff activities, etc. The actualizations of a building include the process of planning and design, construction, assessment, check and accept, running and management. In traditional concepts, people think much of the indoor air issues after using while neglect the effect of planning design and running management stages. How to achieve a good indoor air quality? In fact, the actualization of indoor air quality must analyze the effect of different stages and adopt different technical means in light of building cycle approach. We can see that the key application stage of indoor air quality is the design and running management stage from the technical guidelines of the sustainable building issued by the Ministry of Construction, China. Persisting in controlling strategy of indoor air quality all along during the whole process of building actualization is the feasible and effective measure to solve the air pollution issue.
7.1 The stage of the planning and design
 Major factors that affect indoor air quality for key technology of indoor air quality control in the planning and design stage include the planning and design of building (location and the surrounding environment of building, room function and room location, location of public garbage channels, building materials), decoration design (walls, ceilings, decorative materials of floors), fitment design (furniture, electricity appliances, location of office equipment and its distribution intensity, purification equipment), the design of drainage facilities (water storage equipment, water storage height), staff, design of ventilation system (system form, air form, purification mode and its efficiency, fresh air quantity, location of fresh air collection and approach of fresh air). With the development of simulation technology at present, making pre-assessment to concentration field and temperature field in the design stage can find existent problems in the design effectively and prevent accident occurred. From the point of view of health building and building sustainable development, one of the major ways to improve indoor air environment is controlling the indoor air pollutants effectively and eliminating all sources of pollutants. Moreover, not using polluting materials in the building design is also important. In order to improve the efficiency of natural ventilation in building design, effect on air quality from materials of indoor decoration and fitment should accord with the request of "pollution control criterion of civil environment" (GB5032532001) requirements. Until now, the ventilation is still the most effective means of air purification for civil building.
   In the technical guidelines of the sustainable building issued by the Ministry of Construction, China, technique kernels of planning and design of sustainable building on the part of indoor air quality are stipulated as follows:
   (1) For those building that demand for natural ventilation, space that people often bide to work or dwell in should be natural ventilation. Building design can be combined to enhance the efficiency of the natural ventilation, such as adopting windows that can be turned on, making use of draught, and so on.
   (2) Mounting the position of place with a draught in reason, organizing air flow effectively, taking effective measures to prevent gases colluded with each other and extended, combining full ventilation with part ventilation to avoid polluted air from the kitchen, bathrooms, smoking lounges and other places circulated.
   (3) Impact on indoor air quality from materials of indoor decoration and fitment should accord with the requirements of "Control Criterion of Indoor Environment Pollution" GB50325.
   (4) Making use of new decoration and fitment materials that can improve indoor air quality.
   (5) For those buildings that have concentrated air conditionings, monitoring system of indoor air quality should be mounted to maintain the health and comfort of customers.
   (6) Moreover, some effective measures should be taken to prevent producing dew and growing leaf mold.
7.2 The stage of Construction
 Major problems in construction for key technology of indoor air quality control are as follows: how to select the accessory material effectively, not to use or only use binder containing formaldehyde a little, pay attention to construction according to criterion, at the same time, avoid producing second pollution during the course of construction, avoid the accumulation of dust caused by materials and structure, recover and clean up construction rubbish timely. Environmental awareness should be throughout the whole construction. The construction process of the sustainable building can significantly reduce the interference to the surrounding environment, reduce the quantity of landfill wastes and natural resources consumed in the construction process and reduce the adverse effects to the indoor air quality to the minimum.
7.3 The stages of check and accept and running management
            Monitoring the air quantity index, analyzing cause of problems happened and puting forward the corresponding improvement measures are the sixty-four-dollar questions for key technology of indoor air quality control in the stages of check and accept and running management. At this stage the normal running and maintenance of ventilation systems is especial important to ensure good air quality. In the stage of building running daily, central air conditioning and ventilation equipment should be overhauled and cleaned up promptly. Some facilities in disrepair should be replaced promptly. In addition, people in the room should cultivate good work and life habits, such as no smoking in the room, using the pesticides and other things that are easy to cause air pollution carefully, no sitting in the vicinity of the central air-conditioning vent, paying attention to change the water every day to prevent producing microorganism in the water during the use of humidifier, and so on. In the field of running and maintenance, techniques and methods of sustainable building can ensure goals of building planning and design realized.(5) By setting the reasonable environmental objectives and intelligent system control and making use of scientific and applied consumption patterns, people can ensure running of the building equipment system with security and cleaning, reduce the energy consumption of system, safeguard indoor air quality, thermal environment, acoustic environment and light environment, reduce pollutants in the course of running and increase the running efficiency of the overall building.




8.MAINTAINING INDOOR AIR QUALITY DURING
RENOVATION PROJECTS



8.1.1  Early identification
Early identification of existing building hazards is the first step toward eliminating the development of an IAQ problem. Inspect the area to be renovated during the project planning stage. Look for possible asbestos and lead containing materials which may be disturbed. Attempt to identify sources of dust and microbial contamination. Consult EH&S documentation and arrange for surveys and analyses when appropriate.
Strategy of source management by choosing one or more of the following:
8.1.2  Source Removal
Identify a source of contamination and relocate it so that it will not impact the IAQ. For example, do not locate a diesel generator or a roofing kettle near a building air intake.

8.1.3  Source Substitution
Identify a material likely to impact the IAQ and select a similar but less toxic substitute. Review MSDS’s, manufacturer specifications, and consult with EH&S. For example, choose latex over oil based paint, hardwood over pressed wood, water based over solvent based adhesives, low formaldehyde emitting fabrics, and continuous filament carpet. Consult Boston College Standards for materials which have been reviewed and determined to be acceptable.

8.1.4  Source Encapsulation
Create a barrier around the source and isolate it from other areas of the building so that there is no recirculation of air from the work area into occupied spaces. This may include physically isolating a section of the building with polyethylene sheeting or other barriers, as well as isolating the space from the general ventilation system by blocking return air grilles. Keep doors closed and seal stairwells so that they do not act as conduits for contaminants.

8.1.5  Ventilation
Utilize either dilution ventilation or local exhaust ventilation in conjunction with isolation techniques to reduce contaminant levels. Dilution ventilation increases the amount of outside air passing through an area to dilute and flush out low levels of contaminants. If the building ventilation system will be in contact with the work area, consider installing additional filters to keep particulates out of the ductwork. Change all filters at the conclusion of the project. When strong odors and higher contaminant levels are expected, the area should be encapsulated and placed under negative pressure. This technique isolates the work area from the building ventilation system and uses exhaust fans to directly remove contaminants to the outside. Explosion proof fans must be used while there are flammable chemicals being used in the work area. Positively pressurizing non-work areas and running ventilation systems overnight will minimize contaminant migration into occupied spaces.

8.1.6  Exposure Control
It may be unrealistic to attempt to completely eliminate airborne contaminants during a construction project, but it is possible to minimize occupant exposure to those contaminants by carefully scheduling the work during periods of low occupancy such as holidays, evenings and weekends. In addition, allow for a “flush out” period of ventilation prior to reoccupying the work area. It is recommended that the area be flushed out with maximum outside air at normal temperatures for 72 hours prior to reoccupancy. Increasedventilation may also be warranted for 2 weeks to 2 months post occupancy to remove low level off gassing.Finally, be sensitive to the fact that some individuals are more susceptible to low level contaminants than most, and these people may need to be temporarily relocated. Health Services and occupational health specialists may need to be involved in these determinations.

8.1.7  Housekeeping
Good housekeeping practices will go a long way toward containing dusts and construction debris, and allowing building occupants to feel confident that the project is well managed. Consider using a HEPA filtered vacuum cleaner to minimize recirculation of contaminants. Suppress dust with wet methods. Quickly clean up spilled materials. Protect porous materials such as insulation from exposure to moisture and contaminants.

8.2   Renovation project for

Flooring
Painting
Roofing

8.2.1  Flooring
During flooring operations, existing building materials ( sheet & tile flooring and mastic) which must be removed or prepared must first be examined to see if they are asbestos containing materials (ACM). Consult EH&S or the building survey for this information. Grinding, surfacing, sanding, abrading, breaking or removing ACM flooring may only be done by a licensed asbestos contractor according to all pertinent regulations.
Review the manufacturers specifications on replacement carpet and vinyl flooring and select those with low emission data. New products which are opened and unrolled at the contractors’ facility will emit fewer VOCs upon installation. More importantly, consult the approved products listing and select a low emitting adhesive for flooring installation. Always follow the manufacturers recommendations for use and ventilation. Maintain a copy of the MSDS on site. Minimize the amount of chemical product stored at the construction site, and ensure that containers not in use are kept sealed. Select the most appropriate flooring material for the space. Carpeting used in areas subject to moisture will promote microbial growth contributing to IAQ problems in the future. Implement some combination of the source management techniques to control contaminant levels generated during and after construction.
8.2.2  Painting
Painting operations should begin with the confirmation that the painted surface to be prepared is lead free. Consult EH&S and building surveys for this information. Sanding of lead paint is prohibited and removal may only be done by a licensed deleading contractor according to all pertinent regulations. Select a low VOC emitting paint that is free of lead and mercury. Minimize occupant exposure to interiorpainting by scheduling it during off hours, isolating the space, and ventilating the area well both during and after the painting is completed. Refer to the source management techniques referred to previously.

8.2.3   Roofing
Outdoor work, such as roofing, can also have a significant impact on indoor air quality. Hot tar and hot asphalt materials are intensely odorous, and will generate many complaints if the emissions are drawn intothe building. Locate these sources away from air intakes when feasible, and consider wind patterns. Instructoccupants to keep doors and windows closed. Indoor air intakes may need to be temporarily shut down.Whenever possible, schedule this work during low occupancy periods and provide good communication toall impacted parties which may include neighboring buildings. Roofing materials may also contain asbestos.


       9.HEAT VENTILATION AIR CONTROL   (HVAC) DESIGN
The "green design" movement in the commercial and residential HVAC industry emphasizes paying attention to the issue of indoor air quality throughout the design and construction stages of a building's life.
One technique to reduce energy consumption while maintaining adequate air quality, is demand controlled ventilation. Instead of setting throughput at a fixed air replacement rate, carbon dioxide sensors are used to control the rate dynamically, based on the emissions of actual building occupants.
For the past several years, there have been many debates among indoor air quality specialists about the proper definition of indoor air quality and specifically what constitutes "acceptable" indoor air quality.
One way of quantitatively ensuring the health of indoor air is by the frequency of effective turnover of interior air by replacement with outside air. In the UK, for example, classrooms are required to have 2.5 outdoor air changes per hour. In halls, gym, dining, and physiotherapy spaces, the ventilation should be sufficient to limit carbon dioxide to 1,500 ppm. In the USA, and according to ASHRAE Standards, ventilation in classrooms is based on the amount of outdoor air per occupant plus the amount of outdoor air per unit of floor area, not air changes per hour. Since carbon dioxide indoors comes from occupants and outdoor air, the adequacy of ventilation per occupant is indicated by the concentration indoors minus the concentration outdoors. The value of 615 ppm above the outdoor concentration indicates approximately 15 cubic feet per minute of outdoor air per adult occupant doing sedentary office work where outdoor air contains 385 ppm, the current global average atmospheric CO2 concentration. In classrooms, the requirements in the ASHRAE standard 62.1, Ventilation for Acceptable Indoor Air Quality, would typically result in about 3 air changes per hour, depending on the occupant density. Of course the occupants aren't the only source of pollutants, so outdoor air ventilation may need to be higher when unusual or strong sources of pollution exist indoors. When outdoor air is polluted, then bringing in more outdoor air can actually worsen the overall quality of the indoor air and exacerbate some occupant symptoms related to outdoor air pollution
The use of air filters can trap some of the air pollutants. The Department of Energy's Energy Efficiency and Renewable Energy section wrote "[Air] Filtration should have a Minimum Efficiency Reporting Value (MERV) of 13 as determined by ASHRAE 52.2-1999.Air filters are used to reduce the amount of dust that reaches the wet coils. Dust can serve as food to grow molds on the wet coils and ducts and can reduce the efficiency of the coils.
Moisture management and humidity control requires operating HVAC systems as designed. Moisture management and humidity control may conflict with efforts to try to optimize the operation to conserve energy. For example, Moisture management and humidity control requires systems to be set to supply Make Up Air at lower temperatures (design levels), instead of the higher temperatures sometimes used to conserve energy in cooling-dominated climate conditions. However, for most of the US and many parts of Europe and Japan, during the majority of hours of the year, outdoor air temperatures are cool enough that the air does not need further cooling to provide thermal comfort indoors. However, high humidity outdoors creates the need for careful attention to humidity levels indoors. High humidities give rise to mold growth and moisture indoors is associated with a higher prevalence of occupant respiratory problems.
The "dew point temperature" is an absolute measure of the moisture in air. Some facilities are being designed with the design dew points in the lower 50's °F, and some in the upper and lower 40's °F. Some facilities are being designed using desiccant wheels with gas fired heater to dry out the wheel enough to get the required dew points. On those systems, after the moisture is removed from the make up air, a cooling coil is used to lower the temperature to the desired level.
Commercial buildings, and sometimes residential, are often kept under slightly-positive air pressure relative to the outdoors to reduce infiltration. Limiting infiltration helps with moisture management and humidity control.
Dilution of indoor pollutants with outdoor air is effective to the extent that outdoor air is free of harmful pollutants. Ozone in outdoor air occurs indoors at reduced concentrations because ozone is highly reactive with many chemicals found indoors. The products of the reactions between ozone and many common indoor pollutants include organic compounds that may be more odorous, irritating, or toxic than those from which they are formed. These products of ozone chemistry include formaldehyde, higher molecular weight aldehydes, acidic aerosols, and fine and ultrafine particles, among others. The higher the outdoor ventilation rate, the higher the indoor ozone concentration and the more likely the reactions will occur, but even at low levels, the reactions will take place. This suggests that ozone should be removed from ventilation air, especially in areas where outdoor ozone levels are frequently high. Recent research has shown that mortality and morbidity increase in the general population during periods of higher outdoor ozone and that the threshold for this effect is around 20 parts per billion (ppb).



10.CONCLUSION

Finally, there is enough evidence to accept that indoor air pollution in India is responsible for a high degree ofmorbidity and mortality warranting immediate steps forintervention. The first and the most important step in the prevention of illnesses resulting from the use of biomass fuels is to educate the public, administratorsand politicians to ensure their commitment for the improvement of public health. There is utmo strequirement to collect better and systematic information about actual exposure levels experienced by households in different districts and climatic zones and develop a model for predicting the exposure levels based on fuel use and other household data therein (exposure atlas) to protect the health of children, women and elderly persons.
As most of us spend large part of our life indoor ,indoor air pollution is the major problem to solve and as , such all our effects should be takento minimise and finally eliminate the deleterious effects of indoor air pollution.