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     Anticipating
    The Next Level Of Sophistication In Water Markets 
    Tim
    Cummins and Charles Thompson 
    Tim Cummins and Associates,
    Rosebank, NSW 2480. 
     
    Introduction
    This
    paper is about “markets” in the sense of what demand there may be for
    different sorts of goods and services. It is less concerned with the
    market-place, or the actual process by which buyers and sellers connect with
    each other. Similarly, it is about sophistication in terms of what needs
    will drive markets in the future; more than it is about bringing buyers and
    sellers together with the aid of new technology. 
    Irrigators’
    risk management needs will drive the next level of sophistication in water
    markets. And they will do so quickly. The cap on diversions in the
    Murray-Darling Basin is accelerating what otherwise may have been a relatively
    slow process under the Council of Australian Governments (COAG) nation-wide
    approach to water reform. 
    Those
    reforms guaranteed a market driven future for the water industry. Since they
    were introduced, governments have also concluded that environmental
    sustainability for many of our river systems depends on no further growth in
    diversions. For example, the Murray Darling Basin Ministerial Council has
    agreed to cap Basin water use at the volume required to sustain 1994 levels
    of irrigation development. Caps on diversion have radically altered risk
    management processes in the water industry. 
    Risk Management
    Responsibility Is Being Transferred to Irrigators
    In
    the past, water management agencies calculated seasonal allocations
    according to their understanding of storage levels (and probable inflows)
    combined with their expectations of actual irrigation water use relative to
    announced levels of availability. Prior to the introduction of water
    transfers, water management agencies could be confident that not all of the
    water announced for the season would actually be used. If they did
    underestimate actual usage, the shortfall was offset (at least partially) by
    reducing water for the environment. 
    The
    introduction of water trade initially transferred even greater risk to the
    environment. The increasing activation of “sleeping” and “dozing”
    allocations meant that historic records were no longer reliable guides for
    anticipating future water use. Consequently, actual water usage was more
    likely to be underestimated, and water for the environment was more likely
    to be reduced. 
    Caps
    on diversion stop this growth in environmental risk. They also transfer more
    risk to those irrigators who had been making full use of their seasonal
    allocation. Trade makes it likely that with time all entitlements will be
    activated. Total announced allocations are therefore more likely to match
    actual total water use each season. 
    At
    the same time, water management agencies are starting to take a more
    conservative approach in calculating the total volume available for
    allocation. Previously, seasonal allocations at the start of the irrigation
    season took into account both the volume in storage and the probable inflows
    expected later in the season. From now on, initial seasonal allocations will
    only account for water actually in storage plus an allowance for the minimal
    inflows expected in a dry year. Irrigators will have to make their own risk
    assessments about the probability of allocations increasing during the
    course of the season. 
    Three
    major policy changes: water trading; increased water scarcity (made clear by
    the cap); and more conservative assessments of seasonal allocations, are in
    conjunction. This is dramatically shifting risk management responsibility
    away from water management agencies and shifting it towards individual
    irrigators. 
    The Chicken-and-Egg
    of Different Industries and Different Risks
    Water
    allocation policies have always influenced irrigation farming systems, just
    as irrigation farming systems have always influenced water allocation
    policies. For example, it is interesting to compare and contrast how the
    security of water supply systems have evolved in NSW and Victoria. The NSW
    supply system operates at relatively low security to maximise water use in
    any one year. Victoria’s supply system operates at a higher level of
    security in an effort to ensure base levels of availability for at least two
    years in a row. 
    Have
    the farming systems in the two states developed in response to the security
    with which water authorities have managed systems? Or have the water
    authorities modified the security in response to irrigator needs and wants?
    Are irrigators in NSW willing to take more risk than Victorian irrigators?
    The answer appears to be that security policy has been tailored to the needs
    of the dominant irrigated enterprise mix. Rice, the major irrigated crop in
    southern NSW can accept more risk than dairying, the dominant irrigation
    enterprise in Victoria. 
    The
    most cohesive irrigation industries in the Murray-Darling Basin are rice,
    dairying, cotton and perennial horticulture. Each of those has a different
    irrigation risk profile. 
    Rice
    Rice
    is the dominant irrigation enterprise in the
    southern parts of NSW. Rice based enterprises are mostly irrigated using
    ponded, contour irrigation systems. No other ponded irrigation enterprise is
    currently viable. Switching out of contour irrigation is difficult and
    expensive. Individual rice businesses are generally growing and viable, but
    the dollar return per megalitre is relatively low for the most limiting
    resource (water). 
    Low
    returns per megalitre places reliance on maintaining scale (megalitre/family).
    Before the current NSW water reforms this was relatively easy to achieve,
    but those reforms will reduce average seasonal allocations. This will make
    it more difficult for irrigators to maintain their scales of production.
    When market water prices are low, rice-based enterprises are likely to be
    net buyers of water. 
    Risk
    profiles for rice are dominated by the potential to vary the planted area
    according to water availability. Rice
    enterprises are characterised by: relatively low crop loss per megalitre of
    water shortage, and a low cost/income ratio means that the benefit of
    conserving current water for future seasons is low. 
    Dairy production
    Dairying
    is the most important irrigation enterprise in
    Victoria. On average, Victorian dairy farmers have until now geared their
    enterprises towards a mix of feed sources that makes use of their entire
    water right plus more than 80 per cent extra water in the form of
    “sales”. 
    Under
    current reforms, average “sales” availability will drop by 20 per cent
    and it will be available in fewer years. It seems likely that “sales”
    will become better defined. It will become a separate property right with
    lower security than basic water right. The bottom line is that dairy farmers
    will have to adjust to very significant change. They are likely to be
    significant buyers in the water market. But for the first time they will be
    able to choose a mix of (well defined) high and medium security water
    “products” to suit their individual risk management strategies. 
    The
    high cost/high income ratio for dairying means that the benefits of
    conserving water are higher than for annual cropping enterprises. There is
    also limited capacity to use surplus water by increasing the planted area
    (the enterprise capacity is usually constrained by a limiting resource such
    as herd size rather than water). Moreover, each megalitre reduction in
    seasonal allocation incurs relatively high loss. 
    Cotton
    Cotton
    is the most important irrigation enterprise in southern Queensland and
    northern NSW. Capital investment for cotton production is very high, and
    cotton markets want predictable throughput, therefore irrigators strive for
    consistent production. However, the climatically suitable growing areas
    happen to be within highly variable-flow river systems. Water storages on
    these systems are small relative to average flows, and very small relative
    to peak flows. Therefore, irrigators endeavour to keep water in (on-farm
    & off-farm) storages as long as possible. They use off-allocation flows
    first, in effort to obtain consistent production from “total available”
    water. 
    Although
    water reforms mean greater uncertainty about average annual allocations in
    the medium and long term, the major seasonal risk management strategy is
    likely to remain the same. More cotton will be grown when seasonal
    allocations are high, and less will be grown when seasonal allocations are
    low. Over the long run, some irrigators will try to maintain or improve
    existing allocations by buying extra water. This reinforces the need for
    interstate trade arrangements to be developed between Queensland and NSW. 
    Perennial Horticultural Crops
    Perennial
    crops account for significant volumes of water use in Victoria, NSW and
    South Australia. Water allocation policies in each state have traditionally
    favoured these crops. Nonetheless, Victorian horticulturists now seem
    certain to be exposed to the risk of drought. In a repeat of the last
    hundred years of climatic records, they would endure four years below water
    right. In one year they would be reduced to 60 per cent of water right. 
    The
    prospect for NSW horticulturists appears better but it is subject to some
    uncertainty. On the Murray they are told to expect 100 per cent of their
    volumetric allocation ninety nine years out of a hundred. On the
    Murrumbidgee, they are told to expect 100 per cent of their volumetric
    allocation “in all but the worst drought.” What constitutes the worst
    drought is not specified. Nor is the expected percentage allocation in that
    year specified. 
    South
    Australian horticulturists enjoy a very high level of security. The upper
    states are obliged to pass minimum flows into South Australia even in severe
    droughts. 
    Land
    not water is the limiting resource for horticulturists in normal years. They
    are potential sellers in the temporary market in normal years. Victorian
    horticulturists are likely buyers in the water market in drought years.
    Depending on the true nature of their property rights to water NSW
    horticulturists might also be potential buyers in drought years. However,
    without interstate trade, they may have no one to buy from; because when and
    if their high security allocations were reduced there would be no low
    security water available. 
    Risk Management Is
    Clouded by Uncertainty
    Irrigators
    must deal with many risks. This paper focuses on the risk of their seasonal
    allocation being different to the volumetric allocation. In effect it
    concentrates on the risk of drought. And, to make life simple, it
    concentrates on the relative risks of drought for irrigators throughout the
    Murray-Darling Basin. 
    There
    is a difference between risk and uncertainty. To paraphrase John Maynard
    Keynes: The game of roulette is not subject to uncertainty, but the rate of
    inflation twenty years hence is. He went on to say that for some matters
    there is no scientific basis on which to form any calculable probability
    whatever. We simply do not know! 
    Water
    managers throughout the Murray-Darling Basin have invested heavily in
    understanding the patterns of the past. As responsibility for risk
    management is transferred away from water managers, irrigators are
    developing progressively greater interest in “exceedance levels,”
    “one-in-a-hundred-year droughts,” and the like. This is invaluable
    information, nevertheless it is clouded by what Bernstein (1996) described
    as “nature’s tendency to repeat itself, but only imperfectly.” 
    Models
    of potential water availability are powerful guides to developing risk
    management options, but they can create a sense of unjustified confidence.
    Models are only as good as the weakest source of data used to construct
    them. 
    The
    business of risk management is clouded further still, in some jurisdictions,
    by a perceived lack of transparency about the way the security of water
    entitlements is being calculated. Therefore, for many irrigators, their
    immediate concern is the social and institutional risk that their rights may
    be eroded. They are uncertain about the true nature of their rights. The
    urgency of these concerns makes it difficult for some irrigators to explore
    fully the on-farm risk management options open to them. But if “the essence of risk management lies in maximising the areas where we
    have some control over the outcome, while minimising the areas where we have
    absolutely no control over the outcome …” (Bernstein, 1996), it is
    vital that they do explore their own management options. It is also vital
    for them to be involved in helping to resolve the policy issues. 
    Irrigators Have Four Main
    Risk Management Options 
    Individual
    farmers have four broad strategies for managing irrigation risk. They can: 
    1 -
    Assess the risk in more detail 
    
      - 
        
Analyse
        probability of seasonal allocations being increased later in the season
        (eg using historic records of inflows to storages and tributary inflows)  
      - 
        
Forecast
        weather for the coming season (eg using Southern Oscillation Index data
        and climate predictions)  
     
    2 -
    Improve on-farm water use efficiency 
    
      - 
        
Improve
        irrigation management (e.g. improve irrigation scheduling)  
      - 
        
Improve
        irrigation technology (e.g. install automatic bay gates)  
      - 
        
Substitute
        with other inputs (e.g. buy in more feed for grazing enterprises)  
      - 
        
Change
        other cultural practices  
     
    3 - Use
    alternative water sources 
    
      - 
        
Groundwater  
      - 
        
On-farm
        storages  
     
    4 -
    Trade water 
    
    This
    paper focuses on the trading option. Water trading gives individual
    irrigators considerable scope for irrigation risk management. In the past,
    water management agencies effectively managed risk and assigned uniform risk
    levels to all irrigators in each irrigation industry. From now on,
    individual irrigators will be able to manage their own exposure to the risk
    of drought by buying or selling water entitlements. In so doing, they will
    be substituting the risk of receiving a particular volume of water for the
    risk of having to pay more for that same volume. 
    The
    market price for water as a percentage of the total cost of production is an
    important driver in water trading decisions. In horticulture this will be
    fairly low and is unlikely to change existing plantings, but it may
    influence future development. In dairying it will influence replacement
    strategies such as purchasing feed versus irrigating pastures. In rice and
    mixed farms the market price for water may transform water users into water
    sellers. 
    Markets Can Help Manage
    Risk
    The
    water market is still immature. Its risk management potential has yet to be
    fully explored. For example, it is possible that markets for water
    “futures” and “options” will develop over time. This is predictable
    because trade in such derivatives is usually associated with risk
    management, and the risk of individuals not receiving their full entitlement
    is steadily being more clearly defined and more widely understood.
    Derivatives do not remove the risks that go with owning assets subject to
    volatile markets, but they can determine who takes on the speculation and
    who avoids it 
    Futures
    are contracts for future delivery at specified prices. Options provide the
    opportunity for one side to buy from (or sell to) the other side at a
    prearranged price. 
    Bernstein
    (1996), gives a text book example of how futures work: 
    
       “The
      farmer is helpless before the risk of weather and insects, but he can at
      least escape the uncertainty of what his selling price will be. He can do
      that by selling his crop when he plants it, promising future delivery to
      the buyer at a prearranged price. He may miss out on some profit if prices
      rise, but the futures contract will protect him from catastrophe if prices
      fall. He has passed along the risk of lower prices to someone else. 
       “That
      someone else is often a food processor who faces the opposite risk – he
      will gain if the prices of his inputs fall while the crop is still in the
      ground, but he will be in trouble if prices rise and boost the cost of his
      raw materials. By taking on the farmer’s contract, the processor lets
      the farmer assume that agricultural prices might rise. This transaction,
      involving supposedly risky contracts for both parties, actually lowers
      total risk in the economy.” 
     
    In
    the water industry, there is at least one example of opposite risks. In
    highly regulated streams, for some of the environmental values serviced by
    “environmental water entitlements,” water is effectively most scarce in
    seasons of low to moderate flooding. (River regulation can reduce flood
    height and duration and therefore it can limit environmental benefits.) In
    drought, when water is most scarce for irrigators it is not necessarily
    scarce for those particular environmental values that are being exposed to
    their natural drying cycle. Potentially at least, this offers the basis for
    developing derivatives in water markets. But it is not yet clear to what
    extent “environmental entitlements” could, or should, be traded. Nor is
    it clear how the price of delivering environmental water should be met. 
    In
    practice, relative differences in risk will probably be just as important as
    opposite risks in the development of derivatives. For example, the
    differences in risk profiles between annual crops and permanent horticulture
    in Victoria are certainly large enough to allow the exchange of risks. Even
    within particular industries, risk preferences, risk management options, and
    appropriate skills in decision making will vary. And often there is greater
    variation in profitability within industries than there is between
    industries. 
    Options
    make intuitive sense for the water market. Those with most at stake in the
    event of water shortages, those with high cost/income ratios, could buy call
    options. These options could give them the right, but not the obligation, to
    call on the other side to provide them with water at a prearranged price.
    Those with lower cost/income ratios could buy put
    options that gave them the right to put, or sell, water at a prearranged
    price. 
    The
    buyers of call options would
    effectively be insuring their crop production and insuring against the price
    of water rising. The buyers of put
    options might be prearranging a return from water that is greater than they
    can achieve by irrigating a crop. Or, they may be insuring against the price
    of water falling. 
    Call options would
    presumably be more attractive to those irrigators with contracts to supply
    produce to food processors or wineries. Such contracts are becoming a common
    feature of Australia’s irrigated agriculture. 
    Australia’s Water
    Markets Are Maturing
    Market
    mechanisms were introduced more than a decade ago when water entitlements
    first became separately tradable. The process since then has been
    evolutionary. Pre-existing arrangements have been adapted and modified as
    they revealed themselves inadequate for the new demands placed upon them. In
    that sense, the subsequent change process has itself been market driven. In
    part this evolutionary approach has been deliberate; it has helped build
    community acceptance. But it has also been unavoidable. Any other approach
    would have required a fuller understanding of the market than was possible
    at the time. 
    Water
    markets have gradually evolved to the point where formal market structures
    are being developed to make trade more efficient. For example, water
    exchanges are starting to bring buyers and sellers together in an
    information rich environment. Even if most trade occurs outside these
    exchanges, they still provide “price-posting” for all buyers and sellers
    in the “temporary” water market. 
    More
    than ten years after trade commenced, most jurisdictions are now initiating
    thoroughgoing reviews of the way their water markets operate. There are many
    specific examples of the need for review of institutional arrangements. For
    example, water trade lacks the marketable instruments common to other
    tradable property rights. Land markets are based around “titles,” stock
    markets are based around “scrip,” but water markets are largely based
    around entries in “registers” held by Water Authorities. It is difficult
    to ensure that traded rights actually exist. A marketable instrument would
    allow the overall system to be audited. It would protect against fraud, and
    it would provide investors with confidence in the property right. Water
    property rights need to be explicit (regarding volume and reliability);
    exclusive; enforceable and tradable. 
    Market-Based Approaches
    to Risk Management Will Drive Market Sophistication
    Derivatives
    have a value only in an environment of volatility. Water markets are
    certainly volatile, but we have only a primitive understanding of what
    drives that volatility. The potential buyers and sellers of options would
    want a more sophisticated understanding of the drivers behind demand and
    supply. 
    They
    would want some information in advance. They would want to know the full
    range of industries and valleys with which they might trade. They would want
    information on the ownership and size of entitlements for each valley,
    district and river reach. They would want to know at what stages of the
    season different players were likely to enter the market. They would want to
    know which dates were critical ‘locked in’ dates for different
    enterprises. They would want to know the value of water to each of those
    enterprises. And they would want to detailed information on the methodology
    for determining seasonal allocations. 
    They
    would have to have specific “real-time” information. They would want
    detailed information on usage for each valley, district and river reach.
    They would want information on trading prices, trading volumes and trading
    sentiment. They would want climatic outlooks. And they would want the latest
    readings for the factors affecting seasonal allocation upgrades. 
    Perhaps
    most controversially, trade in water derivatives would invite the
    involvement of people and organisations with sufficient reserves to weather
    some losses in the short-run in the expectation of making money in the
    long-run. Some stakeholders in the water industry would see this as akin to
    insurance companies smoothing volatility for all market players. Others
    would see it as naked speculation. 
    Introducing
    trade in water derivatives would invoke the same sort of controversy that
    surrounded the initial introduction of water trade. 
     
    Acknowledgements
    The
    National Program for Irrigation Research and Development (1999) funded the
    report, “Irrigation Risk Management
    in Current and Future Water Policy Environments,” by Rendell McGuckian,
    Tim Cummins & Associates and Read Sturgess & Associates. It provides
    the basis for much of the information in this paper. 
    Peter
    L Bernstein (1996) wrote the book “Against
    the Gods: the Remarkable Story of Risk” (John Wiley and Sons) that
    informed most of the concepts in this paper. 
    Marsden
    Jacob Associates’ (1999) review of Water
    Trading Development and Monitoring in NSW gave depth to the information
    needs that will drive market sophistication. 
    The
    Victorian Department of Natural Resources and Environment funded various
    studies that have contributed to Tim Cummins’s understanding of water
    markets. 
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