SECTION 8F IRRIGATION WATER QUALITY

Một phần của tài liệu The Water Encyclopedia: Hydrologic Data and Internet Resources - Chapter 8 doc (Trang 115 - 129)

Table 8F.69 Relative Tolerance of Crop Plants to Salt Field Crops

EC!103Z16 EC!103Z10 EC!103Z4

Barley (grain) Rye (grain) Field beans

Sugar beet Wheat (grain)

Rape Oats (grain)

Cotton Rice

Sorghum (grain) Corn (field) Flax Sunflower Castorbeans

EC!103Z10 EC!103Z6

Vegetable Crops

EC!103Z12 EC!103Z10 EC!103Z4

Garden beets Tomato Radish

Kale Broccoli Celery

Asparagus Cabbage Green beans

Spinach Bell pepper

Cauliflower Lettuce Sweet corn

Potatoes (white rose) Carrot

Onion Peas Squash Cucumber

EC!103Z10 EC!103Z4 EC!103Z3

Fruit and Nut Crops

High Salt Tolerance Medium Salt Tolerance Low Salt Tolerance

Date palm Cantaloupe Almond

Fig Apple

Grape Apricot

Jujube Avocado

Olive Blackberry

Papaya Boysenberry

Pineapple Cherimoya

Pomegranate Cherry, sweet

Cherry, sand Currant Gooseberry Grapefruit Lemon Lime Loquat Mango Orange Passion fruit Peach Pear Persimmon Plum: prune

(Continued)

Table 8F.69 (Continued)

High Salt Tolerance Medium Salt Tolerance Low Salt Tolerance Pummelo

Raspberry Rose, apple Sapote, white Strawberry Tangerine

Forage Crops

EC!103Z18 EC!103Z12 EC!103Z4

Alkali sacaton White sweetclover White Dutch clover

Saltgrass Yellow sweetclover Meadow foxtail

Nuttall alkaligrass Perennial ryegrass Alsike clover

Bermuda grass Mountain brome Red clover

Rhodes grass Strawberry clover Ladino clover

Fescue grass Dallis grass Burnet

Canada wild rye Sudan grass

Western wheat- Hubam clover

grass Alfalfa (California common)

Barley (hay) Tall fescue

Bridsfoot trefoil Rye (hay)

Wheat (hay) Oats (hay) Orchardgrass Blue grama Meadow fescue Reed canary Big trefoil Smooth brome Tall meadow oat-grass Cicer milkvetch Sourclover Sickle milkvetch

EC!103Z12 EC!103Z4 EC!103Z2

Note: The numbers following EC!103are the electrical conductivity values of the saturation extract in millimhos per centimeter at 258C associated with a 50-percent decrease in yields. The saturation extract is the solution extracted from a soil at its saturation percentage.

Source: From U.S. Department of Agriculture, 1954; Kandiah, A., FAO, 1987.

C1-S4

C1-S3

C1-S2

C1-S1

C2-S1

C3-S1 C3-S2

C3-S4

C4-S2 C4-S3

C4-S1 C2-S3

C3-S4

C4-S4 C2-S4

C1-S2

100 250 750 2250

Class 0 2 4 6 8 10 12 14 16 18 20 22 24 26 28 30

Sodium Adsorption Ratio (Sar)

Sodium (Alkali) Hazar

d

Medium

HighVery high S4S3S2S1

Low

Medium High Very high

Low

C1 C2 C3 C4

Conductivity

Salinity Hazard

Micromhos/cm (EC X 106) at 250

Figure 8F.20 Quality criteria for irrigation water. Note: Sodium Adsorption Ratio SARZNa/(CaCMg)/2 where concentrations are expressed in millequivalents per liter.

Conductivity

Low-salinity water (C1) can be used for irrigation with most crops on most soils with little likelihood that soil salinity will develop.

Some leaching is required, but this occurs under normal irrigation practices except in soils of extremely low permeability.

Medium-salinity water (C2) can be used if a moderate amount of leaching occurs. Plants with moderate salt tolerance can be grown in most cases without special practices for salinity control.

High-salinity water (C3) cannot be used on soils with restricted drainage. Even with adequate drainage, special management for salinity control may be required and plants with good salt tolerance should be selected.

Very high-salinity water (C4) is not suitable for irrigation under ordinary conditions, but may be used occasionally under very special

circumstances. The soils must be permeable, drainage must be adequate, irrigation water must be applied in excess to provide considerable leaching, and very salt-tolerant crops should be selected.

Sodium

Low-sodium water (S1) can be used for irrigation on almost all soils with little danger of the development of harmful levels of exchangeable sodium. However, sodium-sensitive crops such as stone-fruit trees and avocados may accumulate injurious concentrations of sodium.

Medium-sodium water (S2) will present an appreciable sodium hazard in fine-textured soils having high cation-exchange-capacity, especially under low-leaching conditions, unless gypsum is present in the soil. This water may be used on coarse-textured or organic soils with good permeability.

High-sodium water (S3) may produce harmful levels of exchangeable sodium in most soils and will require special soil management-good drainage, high leaching, and organic matter additions. Gypsiferous soils may not develop harmful levels of exchangeable sodium from such waters. Chemical amendments may be required for replacement of exchangeable sodium, except that amendments may not be feasible with waters of very high salinity.

Very high sodium water (S4) is generally unsatisfactory for irrigation purposes except at low and perhaps medium salinity, where the solution of calcium from the soil or use of gypsum or other amendments may make the use of these waters feasible.

Another criterion for the evaluation of irrigation water is:

Residual Sodium Carbonate (RSC)Z(CO3CHCO3) K(Ca CMg) where concentrations are expressed in meq/liter.

When RSCO2.5 Probably not suitable for irrigation 1.25-2.5 Marginal

!1.25 Probably safe for irrigation. (From U.S. Department of Agriculture.)

Table 8F.70 Guides for Evaluating the Quality of Water Used for Irrigation

Quality Factor Threshold Concentrationa Limiting Concentrationb

Coliform organisms, MPN per 100 mL 1000c —d

Total dissolved solids (TDS), mg/L 500c 1500c

Electrical conductivity,mmhos/cm 750c 2250c

Range of pH 7.0–8.5 6.0–9.0

Sodium adsorption ratio (SAR) 6.0c 15

Residual sodium carbonate (RSC), meq 1.25c 2.5

Arsenic, mg/L 1.0 5.0

Boron, mg/L 0.5c 2.0

Chloride, mg/L 100c 350

Sulfate, mg/L 200c 1000

Copper, mg/L 0.1c 1.0

Note: MPN is most probable number. Sodium absorption ratio is defined by the formula SARZNa/ (CaCMg)/2 where the concentrations are expressed in milliequivalents per liter. Residual sodium carbonate is the sum of the equivalents of normal carbonate and bicarbonate minus the sum of the equivalents of calcium and magnesium.

a Threshold values at which irrigator might become concerned about water quality and might consider using additional water for leaching. Below these values, water should be satisfactory for almost all crops and almost any arable soil.

b Limiting values at which the yield of high-value crops might be reduced drastically, or at which an irrigator might be forced to less valuable crops.

c Values not to be exceeded more than 20 percent of any 20 consecutive samples, nor in any 3 consecutive samples. The frequency of sampling should be specified.

d Aside from fruits and vegetables which are likely to be eaten raw, no limits can be specified. For such crops, the threshold concentration would be limiting.

Source: From Calif. State Water Quality Control Board, 1963.

Table 8F.71 FAO Guidelines for Evaluating the Quality of Water for Irrigation

Potential Irrigation Problem Units

Degree of Restriction on Use

None Slight to Moderate Severe Salinity (affects crop water availability)a

ECW dS/m !0.7 0.7–3.0 O3.0

or TDS mg/L !450 450–2000 O2000

Infiltration (affects infiltration rate of water into the soil. Evaluate using ECWand SAR together)b

SARZ0–3 and ECWZ O0.7 0.7–0.2 !0.2

Z3–6Z O1.2 1.2–0.3 !0.3

Z6–12Z O1.9 1.9–0.5 !0.5

Z12–20Z O2.9 2.9–1.3 !1.3

Z20–40Z O5.0 5.0–2.9 !2.9

Specific Ion Toxicity (affects sensitive crops) Sodium (Na)

Surface irrigation SAR !3 3–9 O9

Sprinkler irrigation me/L !3 O3

Chloride (CI)

Surface irrigation me/L !4 4–10 O10

Sprinkler irrigation me/L !3 !3

Boron (B) mg/L !0.7 0.7–3.0 O3.0

Trace elements (see Table 8F–77)

Miscellaneous Effects (affects susceptible crops)

Nitrogen (NO3-N) mg/L !5 5–30 O30

Bicarbonate (HCO3)(overhead sprinkling only) me/L !1.5 1.5–8.5 O8.5

pH Normal range 6.5–

8.4

a ECWmeans electrical conductivity, a measure of the water salinity, reported in deciSiemens per meter at 258C (dS/m) or in units millimhos per centimeter (mmho/cm). Both are equivalent. TDS means total dissolved solids, reported in milligrams per liter (mg/L).

b SAR means sodium absorption ratio.

Source: From Food and Agriculture Organization of the United Nations, 1985, Water quality for agriculture, irrigation, and drainage paper no. 29. Kandiah, A.,Water Quality in Food Production, Water Quality Bulletin, vol. 12, no. 1, Jan. 1987.

Table 8F.72 Chloride Concentrations (mg/L) Causing Foliar Injury in Crops of Varying Sensitivity

Sensitivity!175

Moderately Sensitive 175–350

Moderately Tolerant

350–700 TolerantO700

Almond Pepper Barley Cauliflower

Apricot Potato Maize Cotton

Citrus Tomato Cucumber Sugar beet

Plum Luceme Sunflower

Grape Safflower

Sorghum

Source: From Australian and New Zealand Environment and Conservation Council and Agriculture and Resource Management Council of Australia and New Zealand, 2000, National Water Quality Management Strategy, Paper No. 4,Australian and New Zealand Guidelines for Fresh and Marine Water Quality, vol. I, The Guidelines, October 2000,www.deh.gov.au.

Original Source: From Mass (1990).

Table 8F.73 Risks of Increasing Cadmium Concentrations in Crops Due to Chloride in Irrigation Waters Irrigation Water Chloride Concentration (mg/L) Risk of Increasing Crop Cadmium Concentrations

0–350 Low

350–750 Medium

O750 High

Note: If high chloride concentrations are present in irrigation water, it is recommended that produce is tested for cadmium concentration in the edible portions (e.g., tubers for potatoes, leaves for leafy vegeatables, grain for cereals, etc).

Source: From Australian and New Zealand Environment and Conservation Council and Agriculture and Resource Management Council of Australia and New Zealand, 2000, National Water Quality Management Strategy, Paper No. 4,Australian and New Zealand Guidelines for Fresh and Marine Water Quality, vol. I, The Guidelines, October 2000,www.deh.gov.au.

Orginal Source: From McLaughlin et al. (1999).

Table 8F.75 Effect of Sodium Expressed as Sodium Adsorption Ratio (SAR) on Crop Yield and Quality under Nonsaline Conditions

Tolerance to SAR and

Range at Which Affected Crop

Growth Response under Field Conditions Extremely sensitive SARZ2–8 Avocado Leaf tip burn, leaf scorch

Deciduous fruits Nuts

Citrus

Sensitive SARZ8–18 Beans Stunted growth

Medium SARZ18–46 Clover Stunted growth, possible

Oats sodium toxicity, possible

Tall fescue calcium or magnesium

Rice deficiency

Dallis grass

High SARZ46–102 Wheat Stunted growth

Cotton Lucerne Barley Beets Rhodes grass Note: SARZSodium Adsorption Ratio.

Source: From Australian and New Zealand Environment and Conservation Council and Agriculture and Resource Management Council of Australia and New Zealand, 2000, National Water Quality Management Strategy, Paper No. 4,Australian and New Zealand Guidelines for Fresh and Marine Water Quality, vol. I, The Guidelines, October 2000,www.deh.gov.au.

Original Source: From Pearson (1960).

Table 8F.74 Sodium Concentration (mg/L) Causing Foliar Injury in Crops of Varying Sensitivity Sensitivity!115

Moderately Sensitive 115–230

Moderately Tolerant

230–460 TolerantO460

Almond Pepper Barley Cauliflower

Apricot Potato Maize Cotton

Citrus Tomato Cucumber Sugar beet

Plum Lucerne Sunflower

Grape Safflower

Sesame Sorghum

Source: From Australian and New Zealand Environment and Conservation Council and Agriculture and Resource Management Council of Australia and New Zealand, 2000,National Water Quality Management Strategy, Paper No. 4,Australian and New Zealand Guidelines for Fresh and Marine Water Quality, vol. I, The Guidelines, October 2000,www.deh.gov.au.

Original Source: From Mass (1990).

Table 8F.76 Limits of Boron in Irrigation Water A. Permissible Limits (Boron in parts per million)

Crop Group

Class of Water Sensitive Semitolerant Tolerant

Excellent

!0.33 !0.67 !1.00 Good

0.33–0.67 0.67–1.33 1.00–2.00 Permissible

0.67–1.00 1.33–2.00 2.00–3.00 Doubtful

1.00–1.25 2.00–2.50 3.00–3.75 Unsuitable

O1.25 O2.50 O3.75

B. Crop Groups of Boron Tolerance (In each group, the plants first named are considered as being more tolerant; the last named, more sensitive.)

Sensitive Semitolerant Tolerant

Pecan Sunflower (native) Athel (Tamarix aphylla)

Walnut (Black; and Persian, or English) Potato Asparagus

Cotton (Acala and Pima) Palm (Phoenix canariensis)

Jerusalem-artichoke Tomato Date palm (P. dactylifera)

Navy bean Sweetpea Sugar beet

American elm Radish Mangel

Plum Field pea Garden beet

Pear Ragged robin rose Alfalfa

Apple Olive Gladiolus

Grape (Sultanina and Malaga) Barley Broadbean

Kadota fig Wheat Onion

Persimmon Corn Turnip

Cherry Milo Cabbage

Peach Oat Lettuce

Apricot Zinnia Carrot

Thornless blackberry Pumpkin

Orange Bell pepper

Avocado Sweet potato

Grapefruit Lima bean

Lemon

Source: From U.S. Dept. of Agriculture.

Table 8F.77 FAO Recommended Maximum Concentrations of Trace Elements in Irrigation Water Element

Recommended Maximum

Concentrationa(mg/L) Remarks

Al 5.0 Can cause nonproductivity in acid soils (pH!5.5), but more alkaline soils atOpH 7.0 will precipitate the lon and eliminate any toxicity

As 0.10 Toxicity to plants varies widely, ranging from 12 mg/L for Sudan grass to less than 0.05 mg/L for rice

Be 0.10 Toxicity to plants varies widely, ranging from 5 mg/L for kale to 0.5 mg/L for bush beans Cd 0.01 Toxic to beans, beets and turnips at concentrations as low as 0.1 mg/L in nutrient

solutions. Conservative limits recommended due to its potential for accumulation in plants and soils to concentrations that may be harmful to humans

Co 0.05 Toxic to tomato plants at 0.1 mg/L in nutrient solution. Tends to be inactivated by neutral and alkaline soils

Cr 0.10 Not generally recognized as an essential growth element. Conservative limits recommended due to lack of knowledge on its toxicity to plants

Cu 0.20 Toxic to a number of plants at 0.1 to 1.0 mg/L in nutrient solutions

F 1.0 Inactivated by neutral and alkaline soils

(Continued)

Table 8F.78 Australian Agricultural Irrigation Water Long-Term Trigger Value (LTV), Short-Term Trigger Value (STV), and Soil Cumulative Contaminant Loading Limit (CCL) Triggers for Heavy Metals and Metalloids

Element

Suggested Soil CCLa (kg/ha)

LTV in Irrigation Water (Long-Term Use—Up to 100 yrs)

(mg/L)

STV in Irrigation Water (Short-Term Use—Up to 20 yrs)

(mg/L)

Aluminum ND 5 20

Arsenic 20 0.1 2.0

Beryllium ND 0.1 0.5

Boron ND 0.5 Refer to table 9.2.18 (Volume 3)

Cadmium 2 0.01 0.05

Chromium ND 0.1 1

Cobalt ND 0.05 0.1

Copper 140 0.2 5

Fluoride ND 1 2

Iron ND 0.2 10

Lead 260 2 5

Lithium ND 2.5 2.5

(0.075 Citrus crops) (0.075 Citrus crops)

Manganese ND 0.2 10

Mercury 2 0.002 0.002

Molybdenum ND 0.01 0.05

Nickel 85 0.2 2

(Continued) Table 8F.77 (Continued)

Element

Recommended Maximum

Concentrationa(mg/L) Remarks

Fe 5.0 Not toxic to plants in aerated soils, but can contribute to soil acidification and loss of availability of essential phosphorus and molybdenum. Overhead sprinkling may result in unsightly deposits on plants, equipment and buildings

Li 2.5 Tolerated by most crops up to mg/L; mobile in soil. Toxic to citrus at low concentrations (0.075 mg/L). Acts similarly to boron

Mn 0.20 Toxic to a number of crops at a few-tenths to a few mg/L, but usually only in acid soils Mo 0.01 Not toxic to plants at normal concentrations in soil and water. Can be toxic to livestock if

forage is grown in soils with high concentrations of available molybdenum Ni 0.20 Toxic to a number of plants at 0.5 mg/L to 1.0 mg/L; reduced toxicity at neutral or

alkaline pH

Pd 5.0 Can inhibit plant cell growth at very high concentrations

Se 0.02 Toxic to plants at concentrations as low as 0.025 mg/L and toxic to livestock if forage is grown in soils with relatively high levels of added selenium. An essential element to animals but in very low concentrations

Sn

Ti Effectively excluded by plants; specific tolerance unknown

W

V 0.10 Toxic to many plants at relatively low concentrations

Zn 2.0 Toxic to many plants at widely varying concentrations; reduced toxicity at pHO6.0 and in fine textured or organic soils

a The maximum concentration is based on a water application rate which is consistent with good irrigation practices (10000 m3/ha/yr). If the water application rate greatly exceeds this, the maximum concentrations should be adjusted downward accordingly. No adjustment should be made for application rates less than 10000 m3/ha/yr. The values given are for water used on a continuous basis at one site.

Source: From Food and Agriculture Organization of the United Nations, 1985, Water quality for agriculture, irrigation, and drainage paper no. 29. Kandiah, A.,Water Quality in Food Production, Water Quality Bulletin, vol. 12, no. 1, Jan. 1987.

Table 8F.78 (Continued)

Element

Suggested Soil CCLa (kg/ha)

LTV in Irrigation Water (Long-Term Use—Up to 100 yrs)

(mg/L)

STV in Irrigation Water (Short-Term Use—Up to 20 yrs)

(mg/L)

Selenium 10 0.02 0.05

Uranium ND 0.01 0.1

Vanadium ND 0.1 0.5

Zinc 300 2 5

Note: Trigger values should only be used in conjunction with information on each individual element and the potential for off-site transport of contaminants.

a NDZNot determined; in sufficient background data to calculate CCL.

Source: From Australian and New Zealand Environment and Conservation Council and Agriculture and Resource Management Council of Australia and New Zealand, 2000,National Water Quality Management Strategy, Paper No. 4,Australian and New Zealand Guidelines for Fresh and Marine Water Quality, vol. I, The Guidelines, October 2000,www.deh.gov.au.

Table 8F.79 Canadian Water Quality Guidelines for the Protection of Agricultural Uses—Irrigation

Parametera Irrigation Water Quality Guideline (mg/L) Dateb

Aldicarb 54.9c 1993

Aluminumd 5000 1987

Arsenice 100f 1997

Atrazine 10f 1989

Berylliumd 100 1987

Borond 500–6000h 1987

Bromacil 0.2f 1997

Bromoxynil 0.33i 1993

Cadmium 5.1i,f 1996

Chlorided 100,000–700,000k 1987

Chlorothalonil 5.8f(other crops) 1984

Chromium 1997

Trivalent chromium (Cr(III)) 4.9f,n 1997

Hexavalent chromium (Cr(VI)) 8n 1987

Cobaltd 50 1987

Coliforms, fecald 100 per 100 mL 1987

Coliforms, totald 1000 per 100 mL 1987

Copperd 200–1000o 1987

Cyanazine 0.5f 1990

Dicamba 0.006 1993

Diclofop-methyl 0.18 1993

Diisopropanolinine 2000f 2005

Dinoseb 16j 1982

Fluorided 1000 1987

Irond 5000 1987

Leadd 200 1987

Linuron 0.071f 1995

Lithiumd 2500 1987

Manganesed 200 1987

MCPA (4-chloro-2-methyI phenoxy acetic acid; 2-MethyI-4-chloro phenoxy acetic acid)

0.0025 1995

Metolachlor 28f 1991

Metribuzin 0.5f 1990

Molybdenumd 10–50r 1987

Seleniumd 20–50s 1987

Simazine 0.5f 1891

Nickeld 200 1987

(Continued)

Table 8F.79 (Continued)

Parametera Irrigation Water Quality Guideline (mg/L) Dateb

Sulfolane 500f 2005

Tebuthiuron 0.27f(cereals) 1995

Total dissolved solids (salinity)d 500,000– 3,500,000t 1887

Uraniumd 10f 1987

Vanadiumd 100 1987

Zincd 1,000–5,000u 1987

Note: ug/L—Micrograms per liter.

a Unless otherwise indicated, supporting documents are available from the guidelines and Standards Division, Environment Canada.

b The guidelines dated 1987 have been carried over fromCanadian Water Quality Guidelines(CCREM 1987) and no fact sheet was prepared. The guidelines dated 1989 to 1997 were developed and initially published in CCREM 1987 as appendixes on the date indicated. They are published as fact sheets in this document. Other guidelines dated 1997 and those dated 1999 are published for the first time in this document.

c Concentration of total aldicarb residues.

d No fact sheet created.

e The technical document for the guideline is available from the Ontario Ministry of the Environment.

f Interim guideline.

h Boron guideline

=500mg LK1for blackberries

=500–1000mg LK1for peaches, cherries, plums, grapes, cowpeas, onions, garlic, sweet potatoes, wheat, barley, sunflowers, mungbeans, sesame, lupins, strawberries, Jerusalem artichokes, kidney beans, and lima beans

=1000–2000mg LK1for red peppers, peas, carrots, radishes, potatoes, and cucumbers

=2000–4000mg LK1for lettuce, cabbage, celery, turnips, Kentucky bluegrass, oats, corn, artichokes, tobacco, mustard, clover, squash, and muskmelons

=4000–6000mg LK1for sorghum, tomatoes, alfalfa, purple vetch, parsley, red beets, and sugar beets

=6000mg LK1for asparagus.

i Guideline value slightly modified from CCREM 1987 + Appendixes due to re-evaluation of the significant figures.

j Guideline is crop-specific (see fact sheet).

k Chloride guideline Foliar damage

=100–178 mg LK1for almond, apricots, and plums

=178–355 mg LK1for grapes, peppers, potatoes, and tomatoes

=355–710 mg LK1for alfalfa, barley, corn, and cucumbers

O710 mg LK1for cauliflower, cotton, safflower, sesame, sorghum, sugar beets, and sunflowers Rootstocks

=180–600 mg LK1for stone fruit (peaches, plums, etc)

=710–900 mg LK1for grapes Cultivars

=110–180 mg LK1for strawberries

=230–460 mg LK1for grapes

=250 mg LK1for boysenberries, blackberries, and raspberries.

n Substance has been re-evaluated since CCREM 1987 + Appendixes. Either a new guideline has been derived or insufficient data existed to derive a new guideline.

o Copper guideline

= 200mg LK1for cereals

= 1000mg LK1for tolerant crops

r Molybdenum guideline = 50mg LK1for short-terms use on acidic soils

s Selenium guideline = 20mg LK1for continuous use

=50mg LK1for intermittent use

t Total dissolved solids guideline =500 mg LK1for strawberries, raspberries, beans, and carrots

=500–800 mg LK1for boysenberries, currants, blackberries, gooseberries, plums, grapes, apricots, peaches, pears, cherries, apples, onions, parsnips, radishes, peas, pumpkins, lettuce, peppers, muskmelons, sweet potatoes, sweet corn, potatoes, celery, cabbage, kohlrabi, cauliflower, cowpeas, broadbeans, flax, sunflowers, and corn

=800–1500 mg LK1 for spinach, cantaloupe, cucumbers, tomatoes, squash, brussels sprouts, broccoli, turnips, smooth brome, alfalfa, big trefoil, beardless wild rye, vetch, timothy, and crested wheat grass

=1500–2500 mg LK1for beets, zucchini, rape, sorghum, oat hay, wheat hay, mountain brome, tall fescue, sweet clover, reed canary grass, birdsfoot trefoil, perennial ryegrass

=3500 mg LK1for asparagus, soybeans, safflower, oats, rye, wheat, sugar beets, barley, barley hay, and tall wheat grass

u Zinc guideline =1000 mg LK1when soil pH!6.5

=5000 mg LK1when soil pHO6.5

Source: From Canadian Council of Ministers of the Environment, 2005, Canadian water quality guidelines for the protection of agricultural water uses: summary table, Updated October 2005. In:Canadian Environmental Quality Guidelines, 1999, Canadian Council of Ministers of the Environment, Winnipeg.

Table 8F.80 Australian Trigger Values for Thermotolerant Coliforms in Irrigation Water Used for Food and Nonfood Crops Intended use

Level of thermotolerant coliformsa (mL)

Raw human food crops in direct contact with irrigation water (e.g. via sprays, irrigation of salad vegetables)

!10 cfub/ 100 Raw human food crops not in direct contact with irrigation water (edible product separated

from contact with water, e.g. by peel, use of trickle irrigation); or crops sold to consumer cooked or processed

!1000 cfu / 100

Pasture and fodder for dairy animals (without withholding period) !100 cfu / 100 Pasture and fodder for dairy animals (with withholding period of 5 days) !1000 cfu / 100 Pasture and fodder (for grazing animals except pigs and dairy animals, i.e. cattle, sheep, and

goats)

!1000 cfu / 100

Silviculture, turf, cotton, etc (restricted public access) !10 000 cfu / 100

a Median values.

b cfuZcolony forming units.

Source: From Australian and New Zealand Environment and Conservation Council and Agriculture and Resource Management Council of Australia and New Zealand, 2000,National Water Quality Management Strategy, Paper No. 4,Australian and New Zealand Guidelines for Fresh and Marine Water Quality, vol. I, The Guidelines, October 2000,www.deh.gov.au.

Original Source: Adapted from ARMCANZ, ANZECC & NHMRC (1999).

Table 8F.81 Australian Agricultural Irrigation Water Long-Term Trigger Value (LTV) and Short- Term Trigger Value (STV) Guidelines for Nitrogen and Phosphorus

Element

LTV in Irrigation Water (Long- Term—up to 100 yrs) (mg/L)

STV in Irrigation Water (Short- Term—up to 20 yrs) (mg/L)

Nitrogen 5 25–125a

Phosphorus 0.05 (To minimise bioclogging of irrigation equipment only)

0.8–12a

a Requires site-specific assessment.

Source: From Australian and New Zealand Environment and Conservation Council and Agriculture and Resource Management Council of Australia and New Zealand, 2000,National Water Quality Management Strategy, Paper No. 4, Australian and New Zealand Guidelines for Fresh and Marine Water Quality, vol. I, The Guidelines, October 2000,www.deh.gov.au.

Table 8F.82 Interim Trigger Value Concentrations for a Range of Herbicides Registered in Australia for Use in or Near Waters Herbicide

Residue Limits in Irrigation Water (mg/L)a

Hazard to Crops from Residue in Waterb

Crop Injury Threshold in Irrigation Water (mg/L)

Acrolein 0.1 C Flood or furrow: beans 60, corn 60,

cotton 80, soybeans 20, sugar- beets 60

Sprinkler: corn 60, soybeans 15, sugar-beets 15, beets

AF 100 C (rutabaga) 3.5, corn 3.5,

Amitrol 0.002 CC lucerne 1600, beans 1200,

carrots 1600, corn 3000, cotton 1600, grains sorghum 800,

Aromatic solvents (Xylene) C oats 2400, potatoes 1300, wheat

1200

Asulam CC

Atrazine CC

Bromazil CCC

Chlorthiamid CC

Copper sulfate C Apparently above concentrations

used for weed control

2,4-D CC Field beans 3.5–10, grapes 0.7–

1.5, sugar-beets 1.0–10

Dicamba CC Cotton 0.18

(Continued)

Một phần của tài liệu The Water Encyclopedia: Hydrologic Data and Internet Resources - Chapter 8 doc (Trang 115 - 129)

Tải bản đầy đủ (PDF)

(224 trang)