| Milking Center Wash Water Treatment |
| Worksheet 10 |
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| Why should I be concerned? |
Dairy wash water is not usually considered a dairy sanitation problem.
If not carefully managed, however, dairy wash water can contaminate both
groundwater and surface water sources.
The amount of wash water generated varies with milking preparation, equipment
used, and the number of cows. A 100-cow, free-stall operation may use anywhere
from 100 to 1000 gallons of water per day in the milking center alone.
Milking center wash water is contaminated with organic matter, nutrients,
chemicals, and microorganisms. Poorly designed or mismanaged wash water
disposal systems can contaminate groundwater and surface water with ammonia,
nitrate, phosphorus, detergents, and disease-causing organisms. If not managed
properly, these contaminants can be carried directly into a well or can
leach through the soil to cause groundwater contamination. Surface water
can also be contaminated by manure, milk solids, ammonia, phosphorus, and
detergents.
The goal of Home·A·Syst is to help you protect the groundwater
that supplies your drinking water. |
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| How will this worksheet help me protect my drinking water? |
- It will take you step-by-step through your milking center wash water
treatment practices.
- It will rank your activities according to how they might affect the
groundwater that provides your drinking water supplies.
- It will provide you with easy-to-understand risk rankings that will
help you analyze your milking center wash water treatment practices.
- It will help you determine which of your practices are reasonably safe
and effective, and which practices might require modification to better
protect your drinking water.
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| How do I complete the worksheet? |
| Follow the directions at the top of the chart on page 3. It should take
you about 15 to 30 minutes to complete this worksheet and summarize your
risk rankings. |
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| Glossary |
Milking Center Wash Water Treatment
These terms may help you make more accurate assessments when completing
worksheet 10. They may also help clarify some of the terms used in fact
sheet 10.
Land application: Application of wash water to croplands and pastures
by irrigation equipment or a liquid manure spreader.
Slow surface infiltration: Application of wash water at one end
of a gently sloping grass filter strip or terrace so that it is treated
as it slowly flows through the plant-soil system. A portion of the flow
percolates to groundwater, and some is used by vegetation.
Soil permeability: The quality that enables the soil to transmit
water or air. Slowly permeable soils have fine-textured materials, like
clays, that permit only slow water movement. Moderately or highly permeable
soils have coarse-textured materials, like sands, that permit rapid water
movement. |
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| Worksheet 10 |
| Milking Center Wash Water Treatment: Assessing Drinking Water
Contamination Risk |
1. Use a pencil. You may want to make changes.
2. For each category listed on the left that is appropriate to your homestead,
read across to the right and circle the statement that best describes conditions
on your homestead. (Skip and leave blank any categories that don't apply
to your homestead.) |
3. Then look above the description you circled to find your rnak number
(4,3,2, or 1) and enter that number in the blank under "your rank."
4. Complete section "What do I do with these rankings?"
5. Allow about 15 to 30 minutes to complete the worksheet and summarize
your risk rankings for milking center wash water treatment practices. |
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LOW RISK
(rank 4) |
LOW-MID RISK
(rank 3) |
MOD-HIGH RISK
(rank 2) |
HIGH RISK
(rank 1) |
YOUR RANK |
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| NO DISCHARGE METHODS (Addressed in fact sheet 10, section 1) |
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| All wash water to manure storage and later applied to fields* |
Wash water delivered directly to liquid manure storage. No discharge expected. |
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Wash water delivered to leaking or frequently overflowing manure storage. |
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| *If using this practice, do not complete the rest of this worksheet. |
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| TREATMENT OF MILKING CENTER WASH WATER BEFORE DISPOSAL (Addressed
in fact sheet 10, section 2) |
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| Milking cleanup practices |
First pipeline rinse captured and added to barn manure. Waste milk never
poured down drain. Manure and excess feed removed from parlor before wash-down. |
Waste milk poured down drain 10 percent of the time. Manure and excess feed
usually removed before wash-down. |
Waste milk poured down drain 50 percent of the time. Manure and excess feed
often washed down drain. |
All waste milk poured down drain emptying into ditch. Manure and excess
feed frequently washed down drain emptying into ditch. |
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| Storage/ settling tank liner |
Concrete or plastic lined. |
Clay lined. |
Cracked or porous liner. |
No liner to prevent seepage. |
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| Settling tank cleanout |
Tank cleaned as needed or every month. |
Tank cleaned every 3-4 months. |
Annual cleaning. |
Tank never cleaned. |
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| Liquid storage period following settling |
9-12 months. |
1 week to 9 months. |
Less than 1 week. |
No storage/settling. Wash water discharged directly to soil as generated. |
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| LAND APPLICATION SITE |
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| Distance from drinking water well |
More than 250 feet downslope from well. |
More than 250 feet upslope from well. |
Less than 250 feet downslope from well. |
Less than 250 feet upslope from well. |
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| DISCHARGE METHODS (Addressed in fact sheet 10, section 3) |
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| Field application |
Applied to growing crops. Nutrient and water needs of crop not exceeded.
Vegetation removed regularly. |
Applied to uncropped fields. Nutrient and water needs of vegetation not
exceeded. Vegetation removed occasionally. |
Applied to cropped or uncropped fields. Plant nutrient needs not exceeded.
Plant water needs exceeded occasionally. Vegetation may or may not be removed. |
Applied consistently to same area. Rates exceed vetetation nutrient and
water needs. Vegetation rarely removed. |
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| Slow surface infiltration |
Combined with high-level pretreatment. Medium- or fine-textured soil (silt
loam, loam, clay loams, clay) more than ten feet to water table or bedrock.
Extended rest period between loadings. Vegetation removed. |
Combined with high- level pretreatment. Medium- or fine-textured soil (silt
loam, loam, clay loams, clay) more than three feet to water table or bedrock.
Extended rest period between loadings. Vegetation removed. |
Some pretreatment. Medium- or fine-textured soil (silt loam, loam, clay
loams, clay) more than two to three feet over bedrock or high water table.
Vegetation not removed. |
No pretreatment. Less than two feet of medium- or fine-textured soil (silt
loam, loam, clay loams, clay) above bedrock or high water table. Vegetation
not removed. |
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| What do I do with these rankings? |
| Step 1: In the table below, summarize your risk scores
by checking the appropriate box for each risk category you answered on this
worksheet. |
| Milking Center Wash Water Treatment Risk Ratings Summary |
| CATEGORY |
Risk |
Low
4 |
3 |
2 |
Risk
1 |
| All wash water to manure storage and later applied to fields |
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| Milking cleanup practices |
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| Storage/settling tank liner |
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| Settling tank cleanout |
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| Liquid storage period |
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| Distance from drinking water well |
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| Field application |
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| Slow surface infiltration |
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Step 2: Look at your rankings for individual activities.
- High risk practices (1's) pose a high risk of polluting groundwater.
- Moderate-to-high risk practices (2's) are inadequate protection
in many circumstances.
- Low-to-moderate risk practices (3's) provide reasonable groundwater
protection.
- Low risk practices (4's) are ideal; should be your goal despite
cost and effort.
Any shaded rankings require immediate attention. Some concerns you can
take care of right away; others could be major or costly projects, requiring
planning and prioritizing before you take action. The long-term goal of
the Home·A·Syst program is to improve homestead practices
and structures so that they are classed as low risk. Activities classed
as low risk generally reflect best management practices.
Transfer any activities that you ranked in the shaded areas in step
1 to the "High-Risk Activities" on pages 2-3 of worksheet 12.
Step 3: Read fact sheet 10, Improving Milking Center Wash Water
Treatment, if you haven't already. Consider how you might modify your homestead
practices to better protect your drinking water. |
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The Homestead Assessment System is a cooperative project of Washington
State University Cooperative Extension, Washington Department of Ecology,
and the U.S. Environmental Protection Agency Region X.
Home·A·Syst team members: Christopher F. Feise
and Edward B. Adams, WSU Cooperative Extension Water Quality Coordinators;
James D. LaSpina, Homestead Assessment System Project Associate.
Milking Center Wash Water Technical Reviewers: Ronald E. Hermanson,
WSU Cooperative Extension; Andy Werkhoven, Dairy Farmer; Anne
Schwartz, Washington Tilth; John A. Gillies, USDA-Soil Conservation
Service; Philip A. KauzLoric, Washington Department of Ecology; John
W. Bernard, WSU Cooperative Extension.
Adapted for Washington from material developed by the Wisconsin, Minnesota,
and Kansas Extension Services and Farm·A·Syst Programs. Washington
Home·A·Syst development was supported by the National Farmstead
Assessment Program.
Issued by Washington State University Cooperative Extension, and the
U.S. Department of Agriculture in furtherance of the Acts of May 8, and
June 30, 1914. Cooperative Extension programs and policies are consistent
with federal and state laws and regulations on nondiscrimination regarding
race, color, religion, national origin, gender, age, disability, and gender
preference. Evidence of noncompliance may be reported through your local
Cooperative Extension office. Trade names have been used to simplify information;
no endorsement is intended. Published September 1993. Subject Code 376.
A. EB1746-W10 |
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