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Lecture No. 09-10

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Lecture No. 09-10 Subject: Alkali-Aggregate Reactivity Certain constituents in aggregates can react harmfully with alkali hydroxides in concrete and cause significant ... – PowerPoint PPT presentation

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Title: Lecture No. 09-10


1
Lecture No. 09-10
2
Subject Alkali-Aggregate Reactivity
  • Certain constituents in aggregates can react
    harmfully with alkali hydroxides in concrete and
    cause significant expansion. There are two forms
    of this reaction
  • Alkali silica reaction (ASR)
  • Alkali-carbonate reaction (ACR)
  • Alkali silica reaction (ASR)
  • Develops by aggregates containing reactive silica
    minerals. This form is more serious and common
    than ACR.

3
ASR
  • ASR has been recognized as a potential source of
    distress in concrete since the late 1930s

4
  • Alkali carbonate reaction (ACR)
  • The aggregates dolomitic (calcium-magnesium
    carbonate) have specific composition that is not
    very common.

5
Alkali silica reaction (ASR)
  • Mechanism
  • The reaction can be visualized as a two-step
    process
  • Alkali hydroxide reactive silica gel ?
    alkali-silica gel
  • Alkali-silica gel moisture ? expansion

6
Alkali silica reaction (ASR)
  • The amount of gel formed in the concrete depends
    on
  • Amount of and type of silica in aggregate.
  • Alkali hydroxide concentration.
  • Sufficient moisture.

7
Alkali silica reaction (ASR)
  • The ASR forms a gel that swells as it draws water
    from the surrounding cement paste (has great
    affinity to moisture). In absorbing water, these
    gels can induce pressure, expansion, and cracking
    of the aggregate and the surrounding paste.
  • The alkali silica gels will fill the microcracked
    regions both within the aggregate and concrete.
    Continued availability of moisture to the
    concrete causes enlargement and extension of the
    microcracks which eventually reach the outer
    surface of the concrete. The crack pattern is
    irregular and referred to as map cracking (see
    Figure 5-20). Or fragments breaking out of the
    surface of the concrete (popouts) as in Figure
    5-21.

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Popouts
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11
Alkali silica reaction (ASR)
  • List of most reactive substances
  • Opal (SiO2 nH2O)
  • Chalcedony (SiO2)
  • Certain forms of quartz (SiO2)
  • Cristobalite (SiO2)

12
Alkali silica reaction (ASR)
  • The most important harmful alkali reactive
    aggregates
  • Opaline cherts
  • Chalcedonic cherts
  • Siliceous limestones
  • Siliceous dolomite

13
Alkali silica reaction (ASR)
  • Identification of Potentially Reactive
    Aggregates
  • Field performance history of structures in
    service for more than 15 years.
  • Different tests can be conducted for initial
    screening and evaluating potential alkali-silica
    reactivity.

14
Alkali silica reaction (ASR)
  • Control of ASR
  • Use of low-alkali Portland cement (less than 0.6
    equivalent Na2O) when alkali-silica reactive
    constituents are suspected to be present in the
    aggregate.
  • If low-alkali cement is not available, the total
    alkali content can be reduced by replacing a part
    of high-alkali cement with supplementary
    cementitious materials such fly ash, ground blast
    furnace slag, and silica fume, or use blended
    cement.

15
Alkali silica reaction (ASR)
  • Control of ASR
  • Wash beach sand and gravel with sweet water to
    insure that the total alkali content from the
    cement and aggregates in concrete does not exceed
    3 kg/m3.
  • Control the access of water to concrete.
  • Replacing 25 - 30 of the reactive sand gravel
    aggregate with crushed limestone (known as
    limestone sweetening).

16
Alkali silica reaction (ASR)
  • Utilization of silica fume, fly ash, and blast
    furnace slag as partial replacement of cement
    will reduce the expansion as shown in Figure
    5-23.

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Aggregate Processing
  • Consists of two stages
  • Basic processing
  • This includes
  • crushing,
  • screening,
  • washing to obtain proper gradation and
    cleanliness.

19
Aggregate Processing
  • Beneficiation (upgrading)
  • Upgrading the quality of the aggregate by
    specific processing methods such as
  • Media separation passing aggregates through a
    heavy liquid with specific gravity less than that
    of the desirable aggregate particles but greater
    than that of the harmful particles.
  • Jigging a process to separate particles with
    small differences in density by pulsating water
    current. Upward pulsations of water through a
    jig (a box with a perforated bottom) move the
    lighter material into a layer on top and then
    removed.

20
Aggregate Processing
  • Rising-current classification separates
    particles with large differences in specific
    gravities. Light materials, such as wood and
    lignite, are floated away in a rapidly upward
    moving stream of water.
  • Crushing used to remove soft and friable
    particles from coarse aggregates.

21
Handling and Storing Aggregates
  • Aggregates should be handled and stored in a way
    that minimizes segregation and degradation and
    prevents contamination by deleterious substances.
    Stockpiles should be built up in thin layers of
    uniform thickness to minimize segregation using
    the truck-dump method. The aggregate is then
    reclaimed with a front-end loader.

22
Handling and Storing Aggregates
  • Whether aggregates are handled by truck, bucket
    loader, clamshell, or conveyor belt, stockpiles
    should not be built up in high, cone-shaped piles
    since this results in segregation..

23
Handling and Storing Aggregates
  • Crushed aggregates segregate less than rounded
    (gravel) aggregates and larger-size aggregates
    segregate more than smaller sizes. To avoid
    segregation of coarse aggregates, size fractions
    can be stockpiled and batched separately.

24
Handling and Storing Aggregates
  • Washed aggregates should be stockpiled in
    sufficient time before use so that they can drain
    to a uniform moisture content. Damp fine material
    has less tendency to segregate than dry material.
  • When dry fine aggregate is dropped from buckets
    or conveyors, the wind can blow out the fines.
    This should be avoided if possible.

25
Marine-Dredged Aggregate
  • When other aggregate sources are not available
    Marine-dredged aggregate, and sand, and gravel
    from the seashore can be used with caution in
    limited concrete applications. Aggregates
    obtained from seabeds have two problems
  • Seashells.
  • Salt.

26
salts
  • The presence of these chlorides may affect the
    concrete by
  • Altering the time of set.
  • Increasing drying shrinkage.
  • Increasing the risk of corrosion of steel
    reinforcement.
  • Causing efflorescence.

27
Seashells
  • The sea shells are hard materials that can
    produce good quality concrete, however, a cement
    content may be required due to angularity of the
    shells to obtain the desired workability.
  • Aggregate containing complete shells should be
    avoided as their presence may result in voids in
    the concrete and lower the compressive strength.

28
Marine-Dredged Aggregate
  • Generally, marine aggregates containing large
    amounts of chloride should not be used in
    reinforced concrete.Marine-dredged aggregates
    can be washed with fresh water to reduce the salt
    content.

29
Recycled Concrete
  • Results in both material and energy savings.
  • The procedure involves
  • (1) Breaking up and removing the old concrete.
  • (2) Crushing in primary and secondary crushers
    (see Figure 5-25).
  • (3) Removing reinforcing steel and embedded items.

30
Crushing concrete with a beamcrsher
31
Recycled Concrete
  • (4) Grading and washing.
  • (5) Finally stockpiling the resulting coarse and
    fine aggregate (see Figure 5-26).

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Recycled Concrete
  • Dirt, gypsum board, wood, and other foreign
    materials should be prevented from contaminating
    the final product.
  • Recycled concrete is primarily used in pavement
    reconstruction.
  • It has been satisfactorily used as an aggregate
    in granular subbases, lean-concrete subbases,
    soil-cement.

35
Recycled Concrete
  • Recycled concrete aggregate generally has a
    higher absorption (3 to 10) and a lower
    relative density than conventional aggregate. The
    absorption values increase as coarse particle
    size decreases (see Figure 5-27).

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Recycled Concrete
  • Recycled concrete aggregate should be tested for
    durability, gradation, and other properties.
  • New concrete made from recycled concrete
    aggregate generally has good durability.
    Carbonation, permeability, and resistance to
    freeze-thaw action have been found to be the same
    or even better than concrete with conventional
    aggregates.

38
Recycled Concrete
  • Drying shrinkage and creep of concrete made with
    recycled aggregates is up to 100 higher than
    concrete with a corresponding conventional
    aggregate. This is due to the large amount of old
    cement paste and mortar especially in the fine
    aggregate.

39
Recycled Concrete
  • Concrete trial mixtures should be made to check
    the new concrete's quality and to determine the
    proper mixture proportions.
  • Frequent monitoring of the properties of recycled
    aggregates should be conducted due to the
    variability in the properties of the old concrete.
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