# Official Journal C 163/2017

| | ISSN 1977-091X |
| --- | --- |
| Official Journal
  of the European Union | C 163 |
| | |
| English edition | Information and Notices | Volume 6023 May 2017 |

ISSN 1977-091X

Official Journal

of the European Union

C 163

English edition

Information and Notices

Volume 6023 May 2017

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| Notice No | Contents | page |
| --- | --- | --- |
| | IV   Notices |
| | NOTICES FROM EUROPEAN UNION INSTITUTIONS, BODIES, OFFICES AND AGENCIES |
| 2017/C 163/01 | Commission notice on guidance document on addressing microbiological risks in fresh fruits and vegetables at primary production through good hygiene | 1 |

Notice No

Contents

page

IV   Notices

NOTICES FROM EUROPEAN UNION INSTITUTIONS, BODIES, OFFICES AND AGENCIES

2017/C 163/01

Commission notice on guidance document on addressing microbiological risks in fresh fruits and vegetables at primary production through good hygiene

1

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| EN | |
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EN

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IV Notices

NOTICES FROM EUROPEAN UNION INSTITUTIONS, BODIES, OFFICES AND AGENCIES

| 23.5.2017 | EN | Official Journal of the European Union | C 163/1 |
| --- | --- | --- | --- |

23.5.2017

EN

Official Journal of the European Union

C 163/1

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Commission notice on guidance document on addressing microbiological risks in fresh fruits and vegetables at primary production through good hygiene

(2017/C 163/01)

CONTENTS

| 1. | Introduction | 2 |
| --- | --- | --- |

1.

| 2. | Objectives of the guidance document | 2 |
| --- | --- | --- |

2.

| 3. | Scope and use | 3 |
| --- | --- | --- |

3.

| 4. | EU legislation applicable | 3 |
| --- | --- | --- |

4.

| 4.1. | Related to General Hygiene rules | 3 |
| --- | --- | --- |

4.1.

| 4.2. | Related to specific EU rules | 3 |
| --- | --- | --- |

4.2.

| 5. | Main risk factors for microbiological pathogens in Fresh Fruits and Vegetables identified by EFSA | 4 |
| --- | --- | --- |

5.

| 6. | Check lists for hygiene inspections of FFV at primary production level | 5 |
| --- | --- | --- |

6.

| 7. | Good agricultural and hygiene practices | 11 |
| --- | --- | --- |

7.

| 7.1. | Control of environmental factors and location of the cropping site | 12 |
| --- | --- | --- |

7.1.

| 7.2. | Control of fertilisers (organic) | 13 |
| --- | --- | --- |

7.2.

| 7.3. | Control of water for primary production and associated operations at the place of such production (harvest and post-harvest) | 17 |
| --- | --- | --- |

7.3.

| 7.4. | Hygiene and health status for agricultural workers | 24 |
| --- | --- | --- |

7.4.

| 7.5. | Control of hygiene conditions during associated activities at farm level in addition to those described in Chapters 7.3 and 7.4 | 26 |
| --- | --- | --- |

7.5.

| 8. | Record keeping and responsibilities for food recalls/withdrawals | 30 |
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8.

| 8.1. | Record keeping | 30 |
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8.1.

| 8.2. | Responsibilities for food recalls/withdrawals | 31 |
| --- | --- | --- |

8.2.

| ANNEX I | Glossary | 32 |
| --- | --- | --- |

ANNEX I

| ANNEX II | Example of matrix to support microbiological risk assessment of agricultural water | 35 |
| --- | --- | --- |

ANNEX II

| ANNEX III | Example of a decision tree to support microbiological risk assessment of agricultural water | 38 |
| --- | --- | --- |

ANNEX III

| Appendix | 39 |
| --- | --- |

1.   INTRODUCTION

According to the 2014 Zoonosis Monitoring Report (1), the majority of verified outbreaks in the EU were associated with foodstuffs of animal origin. Fruit and vegetables were implicated in only 7,1 % of the verified outbreaks, primarily caused by frozen raspberries contaminated with Norovirus, albeit showing an increase compared to 2013 where ‘vegetables and juices’ were reported in 4,4 % of the outbreaks. Nevertheless, the possible consequences of microbiological contamination of fresh fruits and vegetables (FFV) cannot be underestimated as shown by the German crisis (2) linked to the contamination of sprouts by Verotoxin-producing Escherichia coli (VTEC).

In the aftermath of this VTEC crisis in 2011, the Commission asked the European Food Safety Authority (EFSA) to advice on the public health risks posed by pathogens in food of non-animal origin (FNAO), addressing in particular the risk factors and the mitigation options including possible microbiological criteria. As a result, EFSA issued six scientific opinions on the following food/pathogen combinations identified as the most important risks within FNAO:

| (1) | VTEC in seeds and sprouted seeds (3) |
| --- | --- |

(1)

VTEC in seeds and sprouted seeds (3)

| (2) | Salmonella and Norovirus in food of leafy greens eaten raw as salads. |
| --- | --- |

(2)

Salmonella and Norovirus in food of leafy greens eaten raw as salads.

| (3) | Salmonella and Norovirus in berries. |
| --- | --- |

(3)

Salmonella and Norovirus in berries.

| (4) | Salmonella and Norovirus in tomatoes. |
| --- | --- |

(4)

Salmonella and Norovirus in tomatoes.

| (5) | Salmonella in melons. |
| --- | --- |

(5)

Salmonella in melons.

| (6) | Salmonella, Yersinia, Shigella and Norovirus in bulb and stem vegetables, and carrots. |
| --- | --- |

(6)

Salmonella, Yersinia, Shigella and Norovirus in bulb and stem vegetables, and carrots.

This guideline takes account of the relevant opinions of EFSA, and consultation with Member States experts and relevant stakeholders. Though it is intended to offer practical help to growers, it may also be used by official inspectors during their audits where appropriate. EFSA confirmed that further research on possible risks and risk mitigating measures related to FFV should continue.

2.   OBJECTIVES OF THE GUIDANCE DOCUMENT

The purpose of this guidance document is to assist growers (regardless of size) at primary production to apply in a correct and uniform way hygiene requirements related to production and handling of FFV. It will provide guidance to growers on how to address microbiological food safety hazards through good agricultural practices (GAP) and good hygiene practices (GHP) in primary production (i.e. growing, harvest and post-harvest) of FFV sold to consumers raw (unprocessed) or minimally processed (i.e. washed, sorted, packed), including during transportation provided that these activities do not substantially alter their nature as laid down in the definition of Annex I of Regulation (EC) No 852/2004 (4). These activities are hereafter referred to as ‘associated operations’. These good practices should be implemented throughout the primary production chain.

Implementation of this guidance should be considered a priority for any FFV eaten raw and, wherever possible, be aimed at for FFV eaten cooked.

3.   SCOPE AND USE

This Guidance covers the good hygiene practices (GHP) and good agricultural practices (GAP) involved in the production of fresh fruit and vegetables at the primary production level, including associated operations, with the purpose to control microbiological pathogens causing gastrointestinal illness due to the consumption of FFV (5) (e.g. pathogenic E.coli, Hepatitis A virus, Listeria...).

Additional specific guidance for certain produce is included where appropriate (6). As specific EU guidance for good hygiene practice in the production of sprouts and seeds for sprouting (7) is being prepared by the European Sprouted Seeds Association, the production of this category is not further addressed in this guidance.

This guidance document gives guidance as to how to apply the general hygiene requirements in the case of FFV. It should be used in conjunction with other applicable guidance documents. The European FFV industry being very diverse, though the categories of FFV considered hereafter are produced under diverse environmental conditions within the EU Member States and thus some provisions of this guidance might be adjusted to suit small farms, or traditional farming areas, the general hygiene requirements laid down in Annex I of Regulation (EC) No 852/2004 must always be fulfilled.

4.   EU LEGISLATION APPLICABLE

This guidance is specifically dedicated on how to address microbiological hazards. All growers must comply with the relevant EU regulations associated to the practices described in this guide. For a complete understanding, it is essential to recall the most relevant EU legislation for good practices at the primary production of fresh fruit and vegetables.

4.1.   Related to General Hygiene rules

| a. | Regulation (EC) No 178/2002 (8) of 28 January 2002 of the European Parliament and of the Council lays down the general principles and requirements of food law, establishing the European Food Safety Authority and laying down procedures in matters of food safety (generally called ‘the General Food Law’). |
| --- | --- |

a.

Regulation (EC) No 178/2002 (8) of 28 January 2002 of the European Parliament and of the Council lays down the general principles and requirements of food law, establishing the European Food Safety Authority and laying down procedures in matters of food safety (generally called ‘the General Food Law’).

| b. | Regulation (EC) No 852/2004 (9) of the European Parliament and of the Council of 29 April 2004 on the hygiene of foodstuffs lays down general hygiene requirements to be respected by food businesses at all stages of the food chain. All food business operators (all growers are Food Business Operators) have to comply with this Regulation’s requirements for good hygiene practices, aimed at preventing the contamination of food whatever its origin. The scope of this Regulation has been illustrated in the Appendix. |
| --- | --- |

b.

Regulation (EC) No 852/2004 (9) of the European Parliament and of the Council of 29 April 2004 on the hygiene of foodstuffs lays down general hygiene requirements to be respected by food businesses at all stages of the food chain. All food business operators (all growers are Food Business Operators) have to comply with this Regulation’s requirements for good hygiene practices, aimed at preventing the contamination of food whatever its origin. The scope of this Regulation has been illustrated in the Appendix.

4.2.   Related to specific EU rules

| a. | Commission Regulation (EC) No 2073/2005 (10) of 15 November 2005 lays down microbiological criteria for foodstuffs. |
| --- | --- |

a.

Commission Regulation (EC) No 2073/2005 (10) of 15 November 2005 lays down microbiological criteria for foodstuffs.

| b. | Regulation (EC) No 396/2005 (11) of 23 February 2005 of the European Parliament and of the Council lays down maximum residue levels of pesticides in or on food and feed of plant and animal. |
| --- | --- |

b.

Regulation (EC) No 396/2005 (11) of 23 February 2005 of the European Parliament and of the Council lays down maximum residue levels of pesticides in or on food and feed of plant and animal.

| c. | Council Directive 86/278/EEC (12) of 12 June 1986 lays down the use of sewage sludge in agriculture in line with the protection of the environment, and in particular of the soil, as amended by Directive 91/692/EEC, Regulation (EC) No 807/2003 and (EC) No 219/2009. |
| --- | --- |

c.

Council Directive 86/278/EEC (12) of 12 June 1986 lays down the use of sewage sludge in agriculture in line with the protection of the environment, and in particular of the soil, as amended by Directive 91/692/EEC, Regulation (EC) No 807/2003 and (EC) No 219/2009.

| d. | Council Directive 98/83/EC (13) of 3 November 1998 lays down criteria related to the quality of water intended for human consumption. |
| --- | --- |

d.

Council Directive 98/83/EC (13) of 3 November 1998 lays down criteria related to the quality of water intended for human consumption.

| e. | Council Directive 91/676/EEC (14) of 12 December 1991 lays down provisions aiming the protection of waters against pollution caused by nitrates from agricultural sources and preventing further such pollution. |
| --- | --- |

e.

Council Directive 91/676/EEC (14) of 12 December 1991 lays down provisions aiming the protection of waters against pollution caused by nitrates from agricultural sources and preventing further such pollution.

| f. | Regulation (EC) No 1069/2009 (15) of 21 October 2009 lays down health rules as regards animal by-products and derived products not intended for human consumption and repealing Regulation (EC) No 1774/2002 (Animal by-products Regulation). |
| --- | --- |

f.

Regulation (EC) No 1069/2009 (15) of 21 October 2009 lays down health rules as regards animal by-products and derived products not intended for human consumption and repealing Regulation (EC) No 1774/2002 (Animal by-products Regulation).

| g. | Commission Regulation (EU) No 142/2011 (16) of 25 February 2011 implementing Regulation (EC) No 1069/2009 of the European Parliament and of the Council lays down health rules as regards animal by-products and derived products not intended for human consumption. |
| --- | --- |

g.

Commission Regulation (EU) No 142/2011 (16) of 25 February 2011 implementing Regulation (EC) No 1069/2009 of the European Parliament and of the Council lays down health rules as regards animal by-products and derived products not intended for human consumption.

In addition, there are national legislations/standards in place in some Member States (17) regarding the quality of reclaimed water.

Complementary EU hygiene guides are available at DG Sante website/food safety issues. At international level, further information is also available in the Codex Alimentarius codes of hygienic practices relevant for FFV (18).

5.   MAIN RISK FACTORS FOR MICROBIOLOGICAL PATHOGENS IN FRESH FRUITS AND VEGETABLES IDENTIFIED BY EFSA

Flowchart No 1

6.   CHECK LISTS FOR HYGIENE INSPECTIONS OF FFV AT PRIMARY PRODUCTION LEVEL

The example check lists (No 1 to 7) below illustrate the hygiene obligations per risk category (as identified by the EFSA opinions), which any grower can use to check if he fulfils EU hygiene requirements. In addition, these checklists can help growers put in place appropriate recommendations provided in Chapters 6 and 7 of this guide.

Check list No 1: Outcome of official controls and appropriate remedial action

| Control area | Findings | Legislation |
| --- | --- | --- |
| When was the last official control (indicate date)? | | Reg. 852/2004, Annex I, Part A, II.6. |
| In case of non-compliances, has the appropriate remedial action (arising from last official controls) been taken? | |

Control area

Findings

Legislation

When was the last official control (indicate date)?

Reg. 852/2004, Annex I, Part A, II.6.

In case of non-compliances, has the appropriate remedial action (arising from last official controls) been taken?

Check list No 2: Environmental factors and location of the production site

Environmental factors including animal reservoirs are a potential source of contamination of FFV and these risks should be prevented or at least mitigated. In case the analysis signalled a contamination of land, check list No 2 can help growers identify the source of contamination and take the relevant actions to fulfil EU requirements and appropriate recommendations.

| Control area | Findings | Legislation |
| --- | --- | --- |
| Have sources of contamination of land used for growing FFVs been identified? | | Reg. 852/2004, Annex I, Part A,
  II.2, II.3, II.5 (e) |
| Indicate here the source of contamination, if identified and skip the bullet points.
  If NOT, the replies to the following bullet points should help you to identify the source. | |
| — | Is there access by animals (domestic or wild) to growing land? |

Control area

Findings

Legislation

Have sources of contamination of land used for growing FFVs been identified?

Reg. 852/2004, Annex I, Part A,

II.2, II.3, II.5 (e)

Indicate here the source of contamination, if identified and skip the bullet points.

If NOT, the replies to the following bullet points should help you to identify the source.

—

Is there access by animals (domestic or wild) to growing land?

| — | Is there access of animals (domestic or wild) to water sources used in primary production and associated operations? |
| --- | --- |

—

Is there access of animals (domestic or wild) to water sources used in primary production and associated operations?

| — | Is there leaking, leaching or overflowing manure storage areas close to cropping areas? |
| --- | --- |

—

Is there leaking, leaching or overflowing manure storage areas close to cropping areas?

| — | Are there any hazardous waste sites close to cropping areas (currently and in the past)? |
| --- | --- |

—

Are there any hazardous waste sites close to cropping areas (currently and in the past)?

| — | Are there any sewage treatment sites close to cropping areas (currently and in the past)? |
| --- | --- |

—

Are there any sewage treatment sites close to cropping areas (currently and in the past)?

| — | Are there any industrial or mining sites close to cropping areas (currently and in the past)? |
| --- | --- |

—

Are there any industrial or mining sites close to cropping areas (currently and in the past)?

| — | Is there any possibility of runoff from nearby fields? |
| --- | --- |

—

Is there any possibility of runoff from nearby fields?

| — | Is there a possibility of flooding of growing land with contaminated water? |
| --- | --- |

—

Is there a possibility of flooding of growing land with contaminated water?

| — | Is there any surface water surrounding the growing land? |
| --- | --- |

—

Is there any surface water surrounding the growing land?

| — | Are there any other sources of contamination? |
| --- | --- |

—

Are there any other sources of contamination?

Will Primary products undergo any processing that eliminate or reduce contamination to acceptable level?

Yes/No

Reg. 852/2004, Annex I, Part A, II.2, II.3.

If no, processing is to be undertaken to eliminate or reduce the contamination to an acceptable level, it is of utmost importance to follow GHP described in Chapter 6 of this guide.

If a source of contamination has been identified, there is a need to evaluate whether or not the FFV should be grown in this area and if preventive/corrective control measures have been implemented (see examples of measures proposed in Chapter 6 of this Guidance document).

Check list No 3: Fertilisers

| Control area | Findings | Legislation |
| --- | --- | --- |
| If fertilisers are used, specify the type (i.e. organic or inorganic) (19) | | Reg. 852/2004, Annex I, Part A, II. 3(a) and national legislation
  Reg. 1069/2009 (animal by-products reg.) (20)

  Dir. 86/278/EEC (21) on the protection of the environment, and in particular of the soil, when sewage sludge is used in agriculture |
| Are fertilisers stored appropriately? | |
| Are there measures to avoid contamination from organic fertilisers in place? | |
| Indicate which of the following measures are taken to avoid contamination from organic fertilisers: physical, chemical or biological treatments | |
| If composted organic fertilizers from companies are used, is a certificate describing the ‘compost process’ available? | |
| When composting is used, is it done in accordance with the guidelines provided in this document (at least 90 days)? | |
| Is the appropriate time period (pre-harvest interval) between application of untreated manure and harvest of FFV respected?
  NB: it depends on the type of FFV and if it is intended to be eaten raw — see table 1 (e.g. minimum 60 days for fresh leafy greens eaten raw). | |
| If sewage sludge is used, are there control measures and corrective measures in place to avoid microbial contamination? (see table 1) | |
| Are there measures in place to minimize contamination by manure and other natural fertilisers from adjoining fields (e.g. care during application and run-off controls)? If so, please answer the following question. | |
| Specify the measures used to secure areas where manure and other natural fertilisers are treated and stored and to prevent cross-contamination from runoff or leaching (for example barriers may be used to contain the manure and prevent its dispersal). | |
| Where possible, is the equipment, which comes into contact with the manure, washed and disinfected before being used again? | |

Control area

Findings

Legislation

If fertilisers are used, specify the type (i.e. organic or inorganic) (19)

Reg. 852/2004, Annex I, Part A, II. 3(a) and national legislation

Reg. 1069/2009 (animal by-products reg.) (20)

Dir. 86/278/EEC (21) on the protection of the environment, and in particular of the soil, when sewage sludge is used in agriculture

Are fertilisers stored appropriately?

Are there measures to avoid contamination from organic fertilisers in place?

Indicate which of the following measures are taken to avoid contamination from organic fertilisers: physical, chemical or biological treatments

If composted organic fertilizers from companies are used, is a certificate describing the ‘compost process’ available?

When composting is used, is it done in accordance with the guidelines provided in this document (at least 90 days)?

Is the appropriate time period (pre-harvest interval) between application of untreated manure and harvest of FFV respected?

NB: it depends on the type of FFV and if it is intended to be eaten raw — see table 1 (e.g. minimum 60 days for fresh leafy greens eaten raw).

If sewage sludge is used, are there control measures and corrective measures in place to avoid microbial contamination? (see table 1)

Are there measures in place to minimize contamination by manure and other natural fertilisers from adjoining fields (e.g. care during application and run-off controls)? If so, please answer the following question.

Specify the measures used to secure areas where manure and other natural fertilisers are treated and stored and to prevent cross-contamination from runoff or leaching (for example barriers may be used to contain the manure and prevent its dispersal).

Where possible, is the equipment, which comes into contact with the manure, washed and disinfected before being used again?

Check list No 4: Water for primary production and associated operations at the place of such production

| Control area | Findings | Legislation |
| --- | --- | --- |
| Have all sources of water used in your agricultural practices been identified? Indicate the sources (e.g. well, river/stream, reservoirs/swamps/pond, reclaimed water) for all uses (e.g. irrigation, washing, cleaning of equipment etc.) | | Reg. 852/2004, Annex I, Part A, II.2, II.3, II.5 (c) |
| Have distribution systems and storage of water used in your agricultural practices been identified? | |
| Are sources, distribution systems and storage of water protected against contamination (domestic and wild animals, bird droppings...)? | | Reg. 852/2004, Annex I, Part A, II.2, II.3, II.5 (e), II.5 (c) |
| Are water sources and distribution systems used during production isolated from manure and potential runoff? | | Reg. 852/2004, Annex I, Part A, II.2, II.3, II.5 (b) |
| Are sources, distribution systems and storage of water protected against inflow of run-off in case of heavy rainfall? | |
| Are sources, distribution systems and storage of water used in your agricultural practices regularly controlled? (e.g. visual inspection, microbial assessment).
  If yes, how often? | |
| What type of irrigation method is used (e.g. flood irrigation, overhead irrigation and drip irrigation)? | |
| What is the time-interval between the last irrigation and harvest? | |
| Does irrigation water have contact with the edible part of FFV? | |
| Do FFV have physical characteristics that facilitate accumulation of water (e.g. leafy green salads with rough surfaces where water may accumulate)?
  If yes, which action(s) have you taken? | | Reg. 852/2004, Annex I, Part A, II.2, II.3, II.5 (c) |
| Do FFV undergo any post-harvest washing treatment prior to packaging? | | Reg. 852/2004, Annex I, Part A, II.2, II.3, II.5 (b) |
| If FFV undergo post-harvest washing treatment prior to packing, remember that potable water has to be used for the final wash of ready-to-eat FFVs, whereas clean water may be used for initial washing stages. |
| Does the production system allow direct contact between the soil and the edible parts of the crop? | |
| Has a risk assessment been carried out to identify the risk factors of water sources?
  If yes, is it for crop production or/and post-harvest handling? | | Reg. 852/2004, Annex I, Part A, II.2, II.3, II.5 (c) (g) |
| It is important to consider, based on the type of risk, if microbiological testing of the water used in your agricultural practices is necessary (for more explanations see Chapter 6.3 of this Guidance document and Annexes II and III). |
| If microbiological testing of water is carried out:
  Please indicate:






  — | Is it for pathogens and/or indicator microorganisms? |

Control area

Findings

Legislation

Have all sources of water used in your agricultural practices been identified? Indicate the sources (e.g. well, river/stream, reservoirs/swamps/pond, reclaimed water) for all uses (e.g. irrigation, washing, cleaning of equipment etc.)

Reg. 852/2004, Annex I, Part A, II.2, II.3, II.5 (c)

Have distribution systems and storage of water used in your agricultural practices been identified?

Are sources, distribution systems and storage of water protected against contamination (domestic and wild animals, bird droppings...)?

Reg. 852/2004, Annex I, Part A, II.2, II.3, II.5 (e), II.5 (c)

Are water sources and distribution systems used during production isolated from manure and potential runoff?

Reg. 852/2004, Annex I, Part A, II.2, II.3, II.5 (b)

Are sources, distribution systems and storage of water protected against inflow of run-off in case of heavy rainfall?

Are sources, distribution systems and storage of water used in your agricultural practices regularly controlled? (e.g. visual inspection, microbial assessment).

If yes, how often?

What type of irrigation method is used (e.g. flood irrigation, overhead irrigation and drip irrigation)?

What is the time-interval between the last irrigation and harvest?

Does irrigation water have contact with the edible part of FFV?

Do FFV have physical characteristics that facilitate accumulation of water (e.g. leafy green salads with rough surfaces where water may accumulate)?

If yes, which action(s) have you taken?

Reg. 852/2004, Annex I, Part A, II.2, II.3, II.5 (c)

Do FFV undergo any post-harvest washing treatment prior to packaging?

Reg. 852/2004, Annex I, Part A, II.2, II.3, II.5 (b)

If FFV undergo post-harvest washing treatment prior to packing, remember that potable water has to be used for the final wash of ready-to-eat FFVs, whereas clean water may be used for initial washing stages.

Does the production system allow direct contact between the soil and the edible parts of the crop?

Has a risk assessment been carried out to identify the risk factors of water sources?

If yes, is it for crop production or/and post-harvest handling?

Reg. 852/2004, Annex I, Part A, II.2, II.3, II.5 (c) (g)

It is important to consider, based on the type of risk, if microbiological testing of the water used in your agricultural practices is necessary (for more explanations see Chapter 6.3 of this Guidance document and Annexes II and III).

If microbiological testing of water is carried out:

Please indicate:

—

Is it for pathogens and/or indicator microorganisms?

| — | How often is testing performed? |
| --- | --- |

—

How often is testing performed?

| — | Are the data obtained used to elaborate a historical background to determine the most risks sampling points/sampling time? |
| --- | --- |

—

Are the data obtained used to elaborate a historical background to determine the most risks sampling points/sampling time?

Reg. 852/2004, Annex I, Part A, Chapters II.2, II.3, II.5 (g)

Are the water testing results satisfactory?

If the above mentioned results are not satisfactory, have corrective measures been taken?

Reg. 852/2004, Annex I, Part A, II.2, II.3, II.5 (c)

Are there specific control measures for each of the identified risk factors put in place?

Check list No 5: Hygiene and health status for agricultural workers

| Control area | Findings | Legislation |
| --- | --- | --- |
| Has training on personal hygiene and safe food handling practices been provided for staff? Including new or temporary employees | | |
| Are signs to instruct employees to wash their hands posted visibly in appropriate areas? | | Reg. 852/2004, Annex I, Part A, II. 5 (d) |
| When protective equipment is used, is it in appropriate condition and clean? | |
| Is there a policy for handling employee’s illness in place? If yes, please answer the following bullet points. | |
| — | Are personnel aware of not working in contact with produce if they feel unwell, particularly if they have symptoms such as diarrhoea or vomiting? |

Control area

Findings

Legislation

Has training on personal hygiene and safe food handling practices been provided for staff? Including new or temporary employees

Are signs to instruct employees to wash their hands posted visibly in appropriate areas?

Reg. 852/2004, Annex I, Part A, II. 5 (d)

When protective equipment is used, is it in appropriate condition and clean?

Is there a policy for handling employee’s illness in place? If yes, please answer the following bullet points.

—

Are personnel aware of not working in contact with produce if they feel unwell, particularly if they have symptoms such as diarrhoea or vomiting?

| — | Do personnel report any kind of illness or injury to the management? |
| --- | --- |

—

Do personnel report any kind of illness or injury to the management?

| — | Are cuts and wounds covered and protected when personnel are permitted to continue working? |
| --- | --- |

—

Are cuts and wounds covered and protected when personnel are permitted to continue working?

Are areas away from the field and packing lines provided for workers to take breaks and to eat?

Are non-essential persons, casual visitors etc. prevented from accessing the cropping area and other food production areas?

Check list No 6: Hygiene conditions during associated activities at farm level

| Control area | Findings | Legislation |
| --- | --- | --- |
| Is the farm maintained under sanitary conditions and in good repair? | | Reg. 852/2004, Annex I, Part A, II.5 (a), (b). |
| Are toilets and sanitary facilities provided based on the recommendations (22) (workers/number of toilets) and are these segregated from food cropping and production areas? | |
| Are toilets and sanitary facilities suitably located to prevent runoff? | |
| Are toilets and sanitary facilities provided with clean water, soap and means of drying hands? | |
| Are sanitizing gels provided at hand-washing facilities and other appropriate locations? | |
| Is there adequate drainage at the premises to ensure that food contact materials and equipment are not at risk from contamination caused by standing water? | |
| Is waste stored away from the product storage areas to prevent pests? | |
| Are waste containers emptied regularly? | |
| Does non-potable water have a separate system? Is non potable water clearly identified? | | Reg. 852/2004, Annex I, Part A, II.5 (c) |
| Is harvest equipment clean and all equipment and tools that come into direct contact with FFV cleaned and, if appropriate, sanitized regularly as required? | | Reg. 852/2004, Annex I, Part A, II.5 (a) And (b) |
| Are field boxes and product containers only used to hold the product and are they regularly cleaned? | |
| Are product containers suitable for contact with food? | |
| Are containers and equipment kept in good conditions to avoid contamination and damage of product? | |
| Are harvested products protected from wind, rain and sun and moved to a processing or packing facility as soon as possible? | |
| Are harvested FFV stored away from chemicals, animals and other sources of contamination? | |
| Are FFV unfit for human consumption segregated before storage or transport? | |
| Are packaging facilities and equipment kept in a suitably clean condition? | |
| Are control temperature options in place? | |
| Are transport equipment/containers and vehicles kept clean? | |
| Are harvested FFV protected against contamination during transport? | |
| Are loading and transportation carried out in a manner to minimise damage and contamination to FFV that may occur? | |
| Are cleaning and disinfection carried out in a manner and location that will not cause FFV to become contaminated? | |
| Is the effectiveness of cleaning and disinfection of food contact surfaces periodically verified by swabbing? (23) | |
| Are the results of swabbing satisfactory? | |
| Are cleaning chemicals handled and used in accordance with manufacturers’ instructions? | |

Control area

Findings

Legislation

Is the farm maintained under sanitary conditions and in good repair?

Reg. 852/2004, Annex I, Part A, II.5 (a), (b).

Are toilets and sanitary facilities provided based on the recommendations (22) (workers/number of toilets) and are these segregated from food cropping and production areas?

Are toilets and sanitary facilities suitably located to prevent runoff?

Are toilets and sanitary facilities provided with clean water, soap and means of drying hands?

Are sanitizing gels provided at hand-washing facilities and other appropriate locations?

Is there adequate drainage at the premises to ensure that food contact materials and equipment are not at risk from contamination caused by standing water?

Is waste stored away from the product storage areas to prevent pests?

Are waste containers emptied regularly?

Does non-potable water have a separate system? Is non potable water clearly identified?

Reg. 852/2004, Annex I, Part A, II.5 (c)

Is harvest equipment clean and all equipment and tools that come into direct contact with FFV cleaned and, if appropriate, sanitized regularly as required?

Reg. 852/2004, Annex I, Part A, II.5 (a) And (b)

Are field boxes and product containers only used to hold the product and are they regularly cleaned?

Are product containers suitable for contact with food?

Are containers and equipment kept in good conditions to avoid contamination and damage of product?

Are harvested products protected from wind, rain and sun and moved to a processing or packing facility as soon as possible?

Are harvested FFV stored away from chemicals, animals and other sources of contamination?

Are FFV unfit for human consumption segregated before storage or transport?

Are packaging facilities and equipment kept in a suitably clean condition?

Are control temperature options in place?

Are transport equipment/containers and vehicles kept clean?

Are harvested FFV protected against contamination during transport?

Are loading and transportation carried out in a manner to minimise damage and contamination to FFV that may occur?

Are cleaning and disinfection carried out in a manner and location that will not cause FFV to become contaminated?

Is the effectiveness of cleaning and disinfection of food contact surfaces periodically verified by swabbing? (23)

Are the results of swabbing satisfactory?

Are cleaning chemicals handled and used in accordance with manufacturers’ instructions?

Check list No 7: Record keeping and withdrawal/recall procedures

| Control area | Findings | Legislation |
| --- | --- | --- |
| Do you have an accurate record keeping system in place?
  If yes, please answer the following bullet point question(s). | | Reg. 852/2004, Annex I, Part A, III. 9 (a), (b), (c) |
| — | Are there records on the use of pesticides (plant protection products and biocides) in accordance with Article 67 of Regulation (EC) No 1107/2009 (24) and biocides? (Required by legislation) |

Control area

Findings

Legislation

Do you have an accurate record keeping system in place?

If yes, please answer the following bullet point question(s).

Reg. 852/2004, Annex I, Part A, III. 9 (a), (b), (c)

—

Are there records on the use of pesticides (plant protection products and biocides) in accordance with Article 67 of Regulation (EC) No 1107/2009 (24) and biocides? (Required by legislation)

| — | Are there records of the occurrence of pests or diseases that may affect the safety of products of plant origin (Required by legislation)? |
| --- | --- |

—

Are there records of the occurrence of pests or diseases that may affect the safety of products of plant origin (Required by legislation)?

| — | Are results kept of any relevant analyses carried out on samples taken from plants or other samples that have importance to human health (e. g. water quality testing, microbiological analyses of products....) (Required by legislation)? |
| --- | --- |

—

Are results kept of any relevant analyses carried out on samples taken from plants or other samples that have importance to human health (e. g. water quality testing, microbiological analyses of products....) (Required by legislation)?

| — | Are there records for the use of applied fertilisers, including identification of the origin of the fertiliser? |
| --- | --- |

—

Are there records for the use of applied fertilisers, including identification of the origin of the fertiliser?

| — | Are there records for cleaning and disinfection of facilities and equipment? |
| --- | --- |

—

Are there records for cleaning and disinfection of facilities and equipment?

| — | Are there records for staff training in relation to the production of safe food? |
| --- | --- |

—

Are there records for staff training in relation to the production of safe food?

| — | Are there records and a policy for staff returning to work after illness? |
| --- | --- |

—

Are there records and a policy for staff returning to work after illness?

| — | Are there records of temperature control checks and calibration of monitoring equipment? |
| --- | --- |

—

Are there records of temperature control checks and calibration of monitoring equipment?

| — | Are there records on control of the production activities (seed origin, FFV production control data, etc.)? |
| --- | --- |

—

Are there records on control of the production activities (seed origin, FFV production control data, etc.)?

Are appropriate traceability records in place, which enable to trace FFV one step back & one step forward?

Reg. 178/2002 article 18

Are withdrawal and recall procedures in place?

Reg. 178/2002 article 19

Are records available for inspection by the competent authority and receiving food business operators on request?

Reg. 852/2004, Annex I, Part A, III.7

7.   GOOD AGRICULTURAL AND HYGIENE PRACTICES

FFV are grown and harvested under a wide range of climatic conditions and diverse geographical settings. They can be grown in cropping sites indoors (e.g. greenhouses) and outdoors, harvested, and either field-packed or transported to a packing establishment. Production practices, growth conditions and the location of the edible part during growth (soil, soil surface, aerial part) in combination with intrinsic, extrinsic, harvesting and processing factors will affect the final microbiological status of FFV at the time of consumption. It has been shown that microbiological food safety hazards and sources of contamination vary considerably from one type of FFV production to another and from one particular setting/context to another, even for the same FFV. These different factors can be addressed within good agricultural practices and good hygiene practices.

Examples and recommendations on how to implement all the obligations corresponding to Annex I (primary production) of Regulation (EC) No 852/2004 can be found later in this document.

7.1.   Control of environmental factors and location of the cropping site

7.1.1.   General principles

Assessment of environmental risk factors in and around the FFV cropping area (e.g. to identify potential sources of microbiological contamination) is particularly important because subsequent steps may not be adequate to remove contamination that occurs during production and in some cases may lead to conditions that enable the growth of microbiological pathogens.

7.1.2.   EU Obligations set in Regulation (EC) No 852/2004

(Annex I — Part A — II.2) ‘As far as possible, food business operators (FBO) are to ensure that primary products are protected against contamination, having regard to any processing that primary produce will subsequently undergo’.

(Annex I — Part A — II.3 (a))‘...FBO are to comply with appropriate Community and national legislative provisions relating to the control of hazards in primary production and associated operations, including measures to control contamination arising from the air, soil, water, feed, fertilisers, plant protection products and biocides and the storage, handling and disposal of waste.’

(Annex I — Part A — II.5 (e)) ‘FBO producing or harvesting plant products are to take adequate measures, as appropriate, as far as possible to prevent animals and pests from causing contamination.’

7.1.3.   Good practice recommendations

| a. | If a grower suspects a possible risk from the previous use of the primary production area, adjoining sites or industrial activity in the neighbourhood, he should consult technical specialists and the sites may have to be analysed for hazards of concern. |
| --- | --- |

a.

If a grower suspects a possible risk from the previous use of the primary production area, adjoining sites or industrial activity in the neighbourhood, he should consult technical specialists and the sites may have to be analysed for hazards of concern.

| b. | Growers should ensure that cropping areas are properly maintained by removing litter and waste, and by cutting weeds, plant refuse or grass within the immediate vicinity of any building or protective structures that may constitute an attractant, breeding place, or harbourage for pests (25). |
| --- | --- |

b.

Growers should ensure that cropping areas are properly maintained by removing litter and waste, and by cutting weeds, plant refuse or grass within the immediate vicinity of any building or protective structures that may constitute an attractant, breeding place, or harbourage for pests (25).

| c. | Growers should ensure the land surrounding certain protective structures (high tunnel, hoop house, etc.) is cleared from potential sources of contamination for example, plant debris and cull piles should be removed promptly from inside the cropping areas. |
| --- | --- |

c.

Growers should ensure the land surrounding certain protective structures (high tunnel, hoop house, etc.) is cleared from potential sources of contamination for example, plant debris and cull piles should be removed promptly from inside the cropping areas.

| d. | Physical barriers such as mounds, vegetative buffers, and ditches to re-direct or reduce runoff from animal production or waste management operations are recommended as preventive measures to avoid contamination of the cropping area. |
| --- | --- |

d.

Physical barriers such as mounds, vegetative buffers, and ditches to re-direct or reduce runoff from animal production or waste management operations are recommended as preventive measures to avoid contamination of the cropping area.

| e. | Use of distress machines and other repellent equipment, such as those emitting noise or calls (e.g. predator calls, sonic fences and ultrasonic rodent repellents) can reduce animal activity. |
| --- | --- |

e.

Use of distress machines and other repellent equipment, such as those emitting noise or calls (e.g. predator calls, sonic fences and ultrasonic rodent repellents) can reduce animal activity.

| f. | Growers can use scarecrows, mechanical traps, reflective strips or gunshots to ward off birds and pests from contaminating FFVs. If possible, power lines should not run above fields where plants for raw consumption are being cultivated, to avoid contamination from birds perching on the lines. |
| --- | --- |

f.

Growers can use scarecrows, mechanical traps, reflective strips or gunshots to ward off birds and pests from contaminating FFVs. If possible, power lines should not run above fields where plants for raw consumption are being cultivated, to avoid contamination from birds perching on the lines.

| g. | FFV for which the edible (26) part has come into contact with flood waters close to harvest (less than two weeks) should not be consumed as raw product. If the flooding event takes place more than two weeks before harvest or if these products are processed, a case-by-case (site-specific) risk assessment should be performed. |
| --- | --- |

g.

FFV for which the edible (26) part has come into contact with flood waters close to harvest (less than two weeks) should not be consumed as raw product. If the flooding event takes place more than two weeks before harvest or if these products are processed, a case-by-case (site-specific) risk assessment should be performed.

7.2.   Control of fertilisers (organic)

7.2.1.   General principles

The nature of agricultural inputs is very diverse and can include organic fertilisers (e.g. livestock manure, slurries, and sewage sludge) or inorganic fertilisers (chemical fertilisers). Fertilisers should only be applied in sufficient amounts to meet FFV needs. Since the focus of this guide is on microbiological food safety hazards, inorganic fertilisers are not further considered
   (27).

Organic fertilisers are widely and beneficially applied to meet FFV nutrient requirements and improve soil fertility but their incorrect use can be a source of both microbiological (e.g. Salmonella spp., VTEC, Norovirus) and chemical contamination (e.g. heavy metals). Pathogens may be present in manure and other natural fertilisers and may persist for weeks or even months, particularly if treatment of these materials is inadequate.

Physical, chemical or biological treatment methods (e.g. composting (28), pasteurization, heat drying, UV irradiation, alkali digestion, sun drying or combinations of these) may be used to reduce the risk of potential human pathogen survival in manure, sewage sludge and other organic fertilisers.

Organic fertilisers should not therefore contain microbial, physical or chemical contaminants at levels that may adversely affect the safety of FFV and their use must comply with the relevant EU regulations and take account of WHO guidelines on the safe use of wastewater and excreta in agriculture, as appropriate.

7.2.2.   EU Obligations set in Regulation (EC) No 852/2004 and in Directive 86/278/EEC

(Annex I — Part A — II.2) ‘As far as possible, food business growers are to ensure that primary products are protected against contamination, having regard to any processing that primary products will subsequently undergo.’

(Annex I — Part A — II.3 (a)) ‘Food business growers are to comply with appropriate Community and national legislative provisions relating to the control of hazards in primary production and associated operations, including measures to control contamination arising from the air, soil, water, feed, fertilisers, veterinary medicinal products, plant protection products and biocides and the storage, handling and disposal of waste.’

(Annex I — Part A — II.5 (f)) ‘Food business growers producing or harvesting plant products are to take adequate measures, as appropriate to store and handle wastes and hazardous substances so as to prevent contamination.’

(Council Directive 86/278/EEC) ‘The use of sewage sludge in the production of fruits and vegetables must comply with EU and national requirements. In certain situations, sludge may not be used at all in farming, i.e. on fruit and vegetables (FFVs) during the growing season (with the exception of fruit trees) and on soil used to grow fruit and vegetable FFVs that are usually in direct contact with the soil and eaten raw. This ban applies for 10 months before the harvest and during the harvest itself’.

7.2.3.   Good practice recommendations

7.2.3.1.   General recommendations

| a. | All farm holdings should develop a manure management plan (29) identifying where and when manure can and cannot be applied, e.g. areas where manure should not be applied includes around ditches, watercourses, ponds, springs, wells and boreholes, steep slopes with high risk of run-off, environmentally sensitive areas, fields likely to flood etc. |
| --- | --- |

a.

All farm holdings should develop a manure management plan (29) identifying where and when manure can and cannot be applied, e.g. areas where manure should not be applied includes around ditches, watercourses, ponds, springs, wells and boreholes, steep slopes with high risk of run-off, environmentally sensitive areas, fields likely to flood etc.

| b. | When manure, sewage sludge and other organic fertilisers are applied they should be mixed thoroughly with the soil as soon as possible and in any case before drilling and planting the FFV, as this will reduce the potential for direct contamination of FFV, as well as reduce odour and ammonia emissions and potential losses to water. |
| --- | --- |

b.

When manure, sewage sludge and other organic fertilisers are applied they should be mixed thoroughly with the soil as soon as possible and in any case before drilling and planting the FFV, as this will reduce the potential for direct contamination of FFV, as well as reduce odour and ammonia emissions and potential losses to water.

| c. | Avoid locating treatment or storage areas for manure and other organic fertilisers (including storage of sewage sludge) in close proximity to FFV cropping areas. |
| --- | --- |

c.

Avoid locating treatment or storage areas for manure and other organic fertilisers (including storage of sewage sludge) in close proximity to FFV cropping areas.

| d. | Prevent run-off or leaching from treatment and storage areas contaminating surrounding land, surface and ground waters etc., by using adequate physical barriers (e.g. drainage ditches). |
| --- | --- |

d.

Prevent run-off or leaching from treatment and storage areas contaminating surrounding land, surface and ground waters etc., by using adequate physical barriers (e.g. drainage ditches).

| e. | Any equipment that has come into contact with manure, sewage sludge or other organic fertilisers should be thoroughly cleaned and, where appropriate, sanitised before being used again. |
| --- | --- |

e.

Any equipment that has come into contact with manure, sewage sludge or other organic fertilisers should be thoroughly cleaned and, where appropriate, sanitised before being used again.

| f. | As far as possible, farm vehicle movements should be controlled to prevent cross-contamination of cropping and production areas. |
| --- | --- |

f.

As far as possible, farm vehicle movements should be controlled to prevent cross-contamination of cropping and production areas.

| g. | Personnel handling manure and sewage sludge should practice good personal hygiene (e.g. washing hands after working with these materials and before handling FFV, eating or drinking etc.), wear appropriate personal protection equipment and suitable outer clothing, including gloves and waterproof footwear that can be effectively cleaned and disinfected after use. |
| --- | --- |

g.

Personnel handling manure and sewage sludge should practice good personal hygiene (e.g. washing hands after working with these materials and before handling FFV, eating or drinking etc.), wear appropriate personal protection equipment and suitable outer clothing, including gloves and waterproof footwear that can be effectively cleaned and disinfected after use.

7.2.3.2.   Treated manures (e.g. solid manures, slurries)

| a. | Treated manures can be applied to land used to grow FFV eaten raw at any time before drilling/planting (30). |
| --- | --- |

a.

Treated manures can be applied to land used to grow FFV eaten raw at any time before drilling/planting (30).

| b. | In general treated manures should not be applied to FFV after planting. However, where essential to the production system, treated manures can be applied to the soil to meet FFV nutrient requirements during the growing period providing a valid composting process has been used (see guidance on composting below) and there is no direct or indirect contact with the edible parts of FFV. |
| --- | --- |

b.

In general treated manures should not be applied to FFV after planting. However, where essential to the production system, treated manures can be applied to the soil to meet FFV nutrient requirements during the growing period providing a valid composting process has been used (see guidance on composting below) and there is no direct or indirect contact with the edible parts of FFV.

| c. | When using batch stored (or ‘matured’) manure, the storage or passive treatment time will vary depending on the region, climate and origin of the manure. No additions of fresh manure should be made to the store during this storage period. |
| --- | --- |

c.

When using batch stored (or ‘matured’) manure, the storage or passive treatment time will vary depending on the region, climate and origin of the manure. No additions of fresh manure should be made to the store during this storage period.

| d. | Composting of solid manures is a particularly effective method of controlling microbial pathogens when actively managed. It is recommended that manure be treated as a batch and turned regularly (e.g. at least twice within the first 7 days either with a front-end loader or preferably with a purpose-built compost turner). This should generate high temperatures over a period of time (minimum of 55 °C for 3 days) to be effective in killing pathogens. The composted manure should be allowed to mature as part of the process and, in general, the whole process should last at least 3 months prior to use. |
| --- | --- |

d.

Composting of solid manures is a particularly effective method of controlling microbial pathogens when actively managed. It is recommended that manure be treated as a batch and turned regularly (e.g. at least twice within the first 7 days either with a front-end loader or preferably with a purpose-built compost turner). This should generate high temperatures over a period of time (minimum of 55 °C for 3 days) to be effective in killing pathogens. The composted manure should be allowed to mature as part of the process and, in general, the whole process should last at least 3 months prior to use.

| e. | Lime treatment of slurry (addition of quick lime or slaked lime to raise the pH to 12 for at least 2 hours) is an effective method of inactivating bacterial pathogens. The slurry should be allowed to mature as part of the batch treatment process. In general slurry should be matured for at least 3 months prior to use. |
| --- | --- |

e.

Lime treatment of slurry (addition of quick lime or slaked lime to raise the pH to 12 for at least 2 hours) is an effective method of inactivating bacterial pathogens. The slurry should be allowed to mature as part of the batch treatment process. In general slurry should be matured for at least 3 months prior to use.

7.2.3.3.   Untreated or partially-treated manures/other organic fertilisers

| a. | In general the time period between application of untreated or partially-treated manure/other organic fertilisers to land, planting and harvest of FFV eaten raw (pre-harvest interval) should be maximised, as microbial pathogens die off over time. |
| --- | --- |

a.

In general the time period between application of untreated or partially-treated manure/other organic fertilisers to land, planting and harvest of FFV eaten raw (pre-harvest interval) should be maximised, as microbial pathogens die off over time.

| b. | Climate, soil type and origin of manure also affect the survival of pathogens in manure, fertiliser-amended soil and in directly deposited animal faeces (if land has previously been used for grazing). |
| --- | --- |

b.

Climate, soil type and origin of manure also affect the survival of pathogens in manure, fertiliser-amended soil and in directly deposited animal faeces (if land has previously been used for grazing).

| c. | Pre-harvest intervals of 120 days are generally accepted in GAP guidance for fresh leafy greens (31), although a period of 60 days is considered to be the minimum duration. |
| --- | --- |

c.

Pre-harvest intervals of 120 days are generally accepted in GAP guidance for fresh leafy greens (31), although a period of 60 days is considered to be the minimum duration.

| d. | In some cases, pre-harvest intervals of up to 12 months or longer are recommended for FFV eaten raw (e.g. countries with relatively cooler climates and lower levels of solar radiation, such as northern European countries). |
| --- | --- |

d.

In some cases, pre-harvest intervals of up to 12 months or longer are recommended for FFV eaten raw (e.g. countries with relatively cooler climates and lower levels of solar radiation, such as northern European countries).

| e. | Table 1 provides an example of some recommended pre-harvest intervals for application of a range of organic fertilisers (including treated and untreated manures) on different types of FFV eaten raw and cooked. |
| --- | --- |

e.

Table 1 provides an example of some recommended pre-harvest intervals for application of a range of organic fertilisers (including treated and untreated manures) on different types of FFV eaten raw and cooked.

7.2.3.4.   Sewage sludge treatment and application

| a. | Strict controls should be implemented where treated sewage sludge is applied to land growing FFV. Prior to any application, the soil must be tested by the sludge supplier. |
| --- | --- |

a.

Strict controls should be implemented where treated sewage sludge is applied to land growing FFV. Prior to any application, the soil must be tested by the sludge supplier.

| b. | As far as possible the time period between application of treated sewage sludge and harvest (pre-harvest interval) should be maximised and reflect the type of treatment applied (i.e. level of pathogen reduction in treated sewage sludge) and the FFV grown. In general a longer pre-harvest interval is recommended when treatment results in a lower level of pathogen reduction; the FFV grown is normally eaten raw; and when there may be direct contact between the edible part of the FFV and the soil. |
| --- | --- |

b.

As far as possible the time period between application of treated sewage sludge and harvest (pre-harvest interval) should be maximised and reflect the type of treatment applied (i.e. level of pathogen reduction in treated sewage sludge) and the FFV grown. In general a longer pre-harvest interval is recommended when treatment results in a lower level of pathogen reduction; the FFV grown is normally eaten raw; and when there may be direct contact between the edible part of the FFV and the soil.

| c. | Where conventional (32) treated sewage sludge is used, the pre-harvest interval should be at least 30 months for FFV eaten raw or at least 12 months for FFV eaten cooked. |
| --- | --- |

c.

Where conventional (32) treated sewage sludge is used, the pre-harvest interval should be at least 30 months for FFV eaten raw or at least 12 months for FFV eaten cooked.

| d. | Where enhanced (33) treated sewage sludge is used, the recommended pre-harvest interval should be at least 10 months for all FFV eaten both raw and cooked. |
| --- | --- |

d.

Where enhanced (33) treated sewage sludge is used, the recommended pre-harvest interval should be at least 10 months for all FFV eaten both raw and cooked.

7.2.3.5.   Specifications for production and use of anaerobic digestates and composts (34)

| a. | Relevant quality assurance specifications should be developed for anaerobic digestate and compost-based fertilisers purchased from external suppliers, including appropriate microbiological specifications for the final (fertiliser) product. |
| --- | --- |

a.

Relevant quality assurance specifications should be developed for anaerobic digestate and compost-based fertilisers purchased from external suppliers, including appropriate microbiological specifications for the final (fertiliser) product.

| b. | A pasteurisation step should be included in the production of anaerobic digestates, where appropriate. |
| --- | --- |

b.

A pasteurisation step should be included in the production of anaerobic digestates, where appropriate.

| c. | In addition, where possible, standardised protocols should be developed and implemented to cover the production and use of quality assured anaerobic digestates and composts, including specification of appropriate source-segregated organic waste input material (feedstock). |
| --- | --- |

c.

In addition, where possible, standardised protocols should be developed and implemented to cover the production and use of quality assured anaerobic digestates and composts, including specification of appropriate source-segregated organic waste input material (feedstock).

| d. | Growers should pay attention to potential for contamination of input materials and anaerobic digestates/composts with glass, metal or hard plastic especially when the material is applied to land used for growing potatoes and root FFVs. |
| --- | --- |

d.

Growers should pay attention to potential for contamination of input materials and anaerobic digestates/composts with glass, metal or hard plastic especially when the material is applied to land used for growing potatoes and root FFVs.

7.2.3.6.   Due diligence when using organic fertilisers purchased from the market

Growers buying livestock manure, sewage sludge and other organic fertilisers from the market should select a reputable supplier and obtain documentation that identifies the origin, treatment applied, and results of all tests (including for microbiological and chemical contaminants) carried out on the final product.

Table 1 gives an example of pre-harvest intervals that should be followed when growers use organic fertilisers.

Table 1:

| | Anaerobic Digestate (Quality Assured (35) and Pasteurised) | Anaerobic Digestate (Quality Assured, not pasteurised)
  Anaerobic Digestate (not assured) | Raw manure/slurry | Compost (including Quality Assured (36) and non-assured source-segregated green compost and green/food compost)
  Treated (37) manure/slurry | Conventional treated sewage sludge (38) | Enhanced treated sewage sludge (39) | Land where immediate previous use has been as grazing land |
| --- | --- | --- | --- | --- | --- | --- | --- |
| FFVs normally eaten raw with no protective skin (40) | Any time before drilling/planting | Not within 12 months of drilling/planting (*1) | Not within 12 months of harvest and at least 6 months before drilling/planting (*1) | Any time before drilling/planting (41) | Not within 30 months of harvest (*1) | Not within 10 months of harvest | Not within 12 months of harvest and at least 6 months before drilling/planting (*1)
   (1) |
| FFVs normally eaten raw either with a protective skin or grown clear of the ground (42) | Any time before drilling/planting | Not within 12 months of harvest and at least 6 months before drilling/planting (*1) | Not within 12 months of harvest and at least 6 months before drilling/planting (*1) | Any time before drilling/planting (43) | Not within 30 months of harvest (*1) | Not within 10 months of harvest | Not within 12 months of harvest and at least 6 months before drilling/
  planting (*1)
   (1) |
| FFVs always eaten cooked (44) | Any time before drilling/planting | Any time before drilling/planting | Any time before drilling/planting | Any time before drilling/planting | Not within 12 months of harvest (*1) | Not within 10 months of harvest | Any time before drilling/planting |

Anaerobic Digestate (Quality Assured (35) and Pasteurised)

Anaerobic Digestate (Quality Assured, not pasteurised)

Anaerobic Digestate (not assured)

Raw manure/slurry

Compost (including Quality Assured (36) and non-assured source-segregated green compost and green/food compost)

Treated (37) manure/slurry

Conventional treated sewage sludge (38)

Enhanced treated sewage sludge (39)

Land where immediate previous use has been as grazing land

FFVs normally eaten raw with no protective skin (40)

Any time before drilling/planting

Not within 12 months of drilling/planting (*1)

Not within 12 months of harvest and at least 6 months before drilling/planting (*1)

Any time before drilling/planting (41)

Not within 30 months of harvest (*1)

Not within 10 months of harvest

Not within 12 months of harvest and at least 6 months before drilling/planting (*1)
   (1)

FFVs normally eaten raw either with a protective skin or grown clear of the ground (42)

Any time before drilling/planting

Not within 12 months of harvest and at least 6 months before drilling/planting (*1)

Not within 12 months of harvest and at least 6 months before drilling/planting (*1)

Any time before drilling/planting (43)

Not within 30 months of harvest (*1)

Not within 10 months of harvest

Not within 12 months of harvest and at least 6 months before drilling/

planting (*1)
   (1)

FFVs always eaten cooked (44)

Any time before drilling/planting

Any time before drilling/planting

Any time before drilling/planting

Any time before drilling/planting

Not within 12 months of harvest (*1)

Not within 10 months of harvest

Any time before drilling/planting

7.3.   Control of water for primary production and associated operations at the place of such production (harvest and post-harvest)

Several factors linked to the use of water in agriculture may influence the risk of microbial contamination of the FFV, such as: source of water, type of irrigation (drip, sprinkler irrigation, etc.), whether the edible portion of the FFV has direct contact with irrigation water, application of a water treatment by the grower, the timing of irrigation in relation to harvesting, possible access of animals to the source, etc. Another important issue to consider is the stage in the food chain: e.g. can a possible contamination still be eliminated or reduced by e.g. drying out (sun irradiation in the field), washing, etc. Ready-to-eat foods and foods closer to the point of consumption will require water of higher quality.

7.3.1.   General principles

In agricultural practices different sources and quality of water are used for pre-harvest, harvest and post-harvest activities (all together called ‘agricultural water’ — see Flowchart No 2), with each of these having a different effect with regard to microbiological contamination of FFVs. Water of inadequate quality has the potential to be a direct source of contamination and a vehicle for spreading localised contamination in the field, facility, or during transport. Wherever water comes in contact with fresh produce, its quality impacts the potential for pathogen contamination. If pathogens survive on the produce, they may cause foodborne illness. Most associated pathogens related to transmission via water of low quality are enteric bacteria, e.g. Salmonella spp., Campylobacter spp., VTEC and viruses, e.g. Norovirus. E. coli is typically used as an index organism to faecal contamination and elevated levels of E. coli may indicate a higher potential for presence of pathogens.

In addition to the recommendations on water control described in this section, the following should also be considered:

| — | Guidelines for treated wastewater use for irrigation projects developed by ISO (45), |
| --- | --- |

—

Guidelines for treated wastewater use for irrigation projects developed by ISO (45),

| — | FAO recommendations on the quality of irrigation water (46), |
| --- | --- |

—

FAO recommendations on the quality of irrigation water (46),

| — | Guidelines developed by the World Health Organization (WHO) in 2006, for the safe use of wastewater and excreta in agriculture and aquaculture (47). |
| --- | --- |

—

Guidelines developed by the World Health Organization (WHO) in 2006, for the safe use of wastewater and excreta in agriculture and aquaculture (47).

Flowchart No 2: Summary of diversity of types of agricultural water and agricultural practices in EU production of (ready-to-eat) FFV

7.3.2.   EU Obligations set in Regulation (EC) No 852/2004

(Annex I — Part A — II.3 (a)) ‘...FBO are to comply with appropriate Community and national legislative provisions relating to the control of hazards in primary production and associated operations, including measures to control contamination arising from air, soil, water, feed, fertilisers, veterinary medicinal products, plant protection products and biocides and the storage, handling and disposal of waste’.

(Annex I — Part A — II.5 (c)) ‘FBO producing or harvesting plant products are to take adequate measures, as appropriate, to use potable water, or clean water, whenever necessary to prevent contamination’.

7.3.3.   Practical tools to assess the source and the intended use of agricultural water

A risk assessment should be carried out considering the source and the intended use of agricultural water (e.g. irrigation system, FFV characteristics, intended use of FFV...), defining the suitability for agricultural purposes, the recommended microbiological threshold values and the frequency of monitoring as described in Annex II of this guidance document.

For guidance on performing a water risk assessment growers can refer to the approach illustrated in the flowchart No 3 which helps to identify the possible contamination sources of the water at primary production of FFV. This applies to both, irrigation water and water used for associated operations (e.g. pesticide application, fertigation, washing etc.).

A more simplified and quick approach may be to use a ‘decision tree’ such as the one in Annex III of this guidance document, where the outcome takes into account a limited number of sampling recommendations compared to those contained in Annex II.

Both tools may be used to take decisions based on the risk profile of agricultural water, but as the two approaches are different, the results cannot be comparable or extrapolated.

Steps that any grower could use to identify possible contamination sources via water at primary production of FFV are summarised in the flowchart No 3 below.

Flowchart No 3: Practical way for the risk assessment of agricultural water

A practical way to carry out the risk assessment of agricultural water in flowchart No 3 is to complete the following table.

Table 2: Application of the general principles of preventing microbiological contamination via water used during agricultural activities

| Activity | Source of water (48) | Outcome of risk assessment (based on Annex II or Annex III) | Need for water testing (based on Annex II and Annex III) and if so, frequency of testing on E. coli/100 ml water |
| --- | --- | --- | --- |
| Pre-harvest |
| Pesticide dilution | | | |
| Cleaning equipment | | | |
| Irrigation | | | |
| Application of fertilizer | | | |
| Dilution of agricultural chemical | | | |
| ... | | | |
| Harvest |
| Cleaning equipment | | | |
| Hand washing of workers for manual harvesting or picking | | | |
| ... | | | |
| Post-harvest |
| Cooling | | | |
| Transport | | | |
| Washing/
  Rinsing | | | |
| Cleaning equipment | | | |
| .... | | | |

Activity

Source of water (48)

Outcome of risk assessment (based on Annex II or Annex III)

Need for water testing (based on Annex II and Annex III) and if so, frequency of testing on E. coli/100 ml water

Pre-harvest

Pesticide dilution

Cleaning equipment

Irrigation

Application of fertilizer

Dilution of agricultural chemical

...

Harvest

Cleaning equipment

Hand washing of workers for manual harvesting or picking

...

Post-harvest

Cooling

Transport

Washing/

Rinsing

Cleaning equipment

....

In order to comply with the EU obligations (see Section 7.3.2), the results of this risk assessment will help by defining the extent to which GHP should be applied (7.3.3) including recommendations on the analyses of the water for agricultural use.

7.3.4.   Good practice recommendations

7.3.4.1.   General recommendations for source, storage and distribution of water

| a. | Untreated (urban) sewage water should not be used. Before considering the use of any other waste water, competent authorities should be consulted as legal restrictions may apply. |
| --- | --- |

a.

Untreated (urban) sewage water should not be used. Before considering the use of any other waste water, competent authorities should be consulted as legal restrictions may apply.

| b. | The quality of agricultural water possibly reused at farm level should be tested. If necessary, the water should be treated and/or disinfected before reuse. |
| --- | --- |

b.

The quality of agricultural water possibly reused at farm level should be tested. If necessary, the water should be treated and/or disinfected before reuse.

| c. | Livestock access to water sources and pumping areas should be avoided. |
| --- | --- |

c.

Livestock access to water sources and pumping areas should be avoided.

| d. | Barriers should be constructed to prevent, as far as possible, wildlife access to waters used in the primary production of FFV. |
| --- | --- |

d.

Barriers should be constructed to prevent, as far as possible, wildlife access to waters used in the primary production of FFV.

| e. | An assessment of the possibilities for contamination of the soil and water by surface water run-off at times of heavy rainfall is recommended, and that structures are built to retain this run-off (barriers formed of strips of vegetation, use of drainage channels, etc.). |
| --- | --- |

e.

An assessment of the possibilities for contamination of the soil and water by surface water run-off at times of heavy rainfall is recommended, and that structures are built to retain this run-off (barriers formed of strips of vegetation, use of drainage channels, etc.).

| f. | Water delivery systems including basins, tanks and storage of water sources should be maintained and cleaned appropriately, to prevent microbial contamination of water and biofilm formation. |
| --- | --- |

f.

Water delivery systems including basins, tanks and storage of water sources should be maintained and cleaned appropriately, to prevent microbial contamination of water and biofilm formation.

| g. | Locate latrines and store manure, faecal waste and fertilisers downhill and at least 250 meters away from water sources to prevent contamination. If needed, growers should assess local situations and foresee a longer distance. |
| --- | --- |

g.

Locate latrines and store manure, faecal waste and fertilisers downhill and at least 250 meters away from water sources to prevent contamination. If needed, growers should assess local situations and foresee a longer distance.

| h. | If the microbiological test result of the water source is unfavourable or a problem has been identified the following corrective measures should be further applied, depending on the source of water:






  i. | Regarding groundwater collected from wells, the following specific measures should be considered:






  — | Regular maintenance of wells. |
| --- | --- | --- | --- |

h.

If the microbiological test result of the water source is unfavourable or a problem has been identified the following corrective measures should be further applied, depending on the source of water:

i.

Regarding groundwater collected from wells, the following specific measures should be considered:

—

Regular maintenance of wells.

| — | Verify that there is a proper separation between the well and the following: domestic waste systems, chemical storage facilities, animal buildings (such as kennel, barnyards, and feed lot facilities), toilets, septic or holding tank, liquid manure and organic fertiliser treatment and storage areas. |
| --- | --- |

—

Verify that there is a proper separation between the well and the following: domestic waste systems, chemical storage facilities, animal buildings (such as kennel, barnyards, and feed lot facilities), toilets, septic or holding tank, liquid manure and organic fertiliser treatment and storage areas.

| — | Check the well casing or well cap on a regular basis to ensure there are no cracks or damage to the well casing or well cap, and the well cap fits tightly. The top of the well should be at least 30 cm above the ground to prevent surface water or contaminants from entering the well. Ensure that the area around the wellhead slopes away from the well and is free of leaves, grass and other debris. |
| --- | --- |

—

Check the well casing or well cap on a regular basis to ensure there are no cracks or damage to the well casing or well cap, and the well cap fits tightly. The top of the well should be at least 30 cm above the ground to prevent surface water or contaminants from entering the well. Ensure that the area around the wellhead slopes away from the well and is free of leaves, grass and other debris.

| — | Build a concrete apron (1 meter radius) around the well or hand pumps. |
| --- | --- |

—

Build a concrete apron (1 meter radius) around the well or hand pumps.

| — | Disinfect the plumbing system (with Chlorine-based sanitizers or other disinfection treatments, for example). |
| --- | --- |

—

Disinfect the plumbing system (with Chlorine-based sanitizers or other disinfection treatments, for example).

| — | If mitigation strategies put in place are not sufficient to avoid contamination of the water source, reparation or construction of new wells should be considered. |
| --- | --- |

—

If mitigation strategies put in place are not sufficient to avoid contamination of the water source, reparation or construction of new wells should be considered.

| ii. | Regarding rainwater, the following specific measures should be considered:






  — | Protect open rainwater storage tanks with meshes to prevent contamination by debris, leaves, animals, and the breeding of insects (insects can be vectors for transmission of microbial contamination). |
| --- | --- | --- |

ii.

Regarding rainwater, the following specific measures should be considered:

—

Protect open rainwater storage tanks with meshes to prevent contamination by debris, leaves, animals, and the breeding of insects (insects can be vectors for transmission of microbial contamination).

| — | Clean on a regular basis, or increase the frequency of cleaning, of open rainwater storage tanks, catchments and gutters of the harvesting systems to collect and maintain good quality rainwater. |
| --- | --- |

—

Clean on a regular basis, or increase the frequency of cleaning, of open rainwater storage tanks, catchments and gutters of the harvesting systems to collect and maintain good quality rainwater.

| — | Change the storage tanks or gutters as necessary. |
| --- | --- |

—

Change the storage tanks or gutters as necessary.

| iii. | Regarding water treatment (primary, secondary treatment and/or water disinfection),the following specific measures should be considered:-






  — | Check the efficacy of water-treatment equipment that is in use. |
| --- | --- | --- |

iii.

Regarding water treatment (primary, secondary treatment and/or water disinfection),the following specific measures should be considered:-

—

Check the efficacy of water-treatment equipment that is in use.

| — | Disinfect the water treatment installations (e.g. by application of biocide or sanitizer) or change the cisterns and plumbing systems of locally collected water. |
| --- | --- |

—

Disinfect the water treatment installations (e.g. by application of biocide or sanitizer) or change the cisterns and plumbing systems of locally collected water.

| — | Change the water-treatment equipment. |
| --- | --- |

—

Change the water-treatment equipment.

| — | If a grower wants to treats or to disinfect the water for producing potable water or to improve its quality, he has to fulfil the requirements of the Regulations on Biocides (49). |
| --- | --- |

—

If a grower wants to treats or to disinfect the water for producing potable water or to improve its quality, he has to fulfil the requirements of the Regulations on Biocides (49).

7.3.4.2.   Good practice recommendations regarding irrigation methods

| a. | For drip-irrigation, pools of water should be avoided on the soil surface or in furrows that may come into contact with the edible portion of the FFV (50). |
| --- | --- |

a.

For drip-irrigation, pools of water should be avoided on the soil surface or in furrows that may come into contact with the edible portion of the FFV (50).

| b. | For overhead irrigation, a higher quality of water should be used as it comes into direct contact with the edible parts of the plant and if possible (51) only at the early stages of plant growth. A time interval between irrigation period and harvest can be applied. This is the case for all products eaten raw (leaf products, vegetables for salads, fruit, etc.) (See risk assessment of agricultural water in 7.3.3). |
| --- | --- |

b.

For overhead irrigation, a higher quality of water should be used as it comes into direct contact with the edible parts of the plant and if possible (51) only at the early stages of plant growth. A time interval between irrigation period and harvest can be applied. This is the case for all products eaten raw (leaf products, vegetables for salads, fruit, etc.) (See risk assessment of agricultural water in 7.3.3).

| c. | The quality of the water use for soil-less systems should be regularly checked and should be changed frequently, or if recycled, it should be treated to minimize microbial contamination. If no compliance with indicators is observed, mitigation strategies mostly based on water treatment technique should be put in place. |
| --- | --- |

c.

The quality of the water use for soil-less systems should be regularly checked and should be changed frequently, or if recycled, it should be treated to minimize microbial contamination. If no compliance with indicators is observed, mitigation strategies mostly based on water treatment technique should be put in place.

| d. | With regard to irrigation systems:






  i. | Flush the main, sub-main and other irrigation lines on a regular basis to reduce accumulation of organic materials or biofilms. It is recommended that the dripper line remains open for at least 1 minute, until the water runs clear. |
| --- | --- | --- |

d.

With regard to irrigation systems:

i.

Flush the main, sub-main and other irrigation lines on a regular basis to reduce accumulation of organic materials or biofilms. It is recommended that the dripper line remains open for at least 1 minute, until the water runs clear.

| ii. | When there is a very intense and long rainy period, it is recommended to flush the system prior to the beginning of the next irrigation season. |
| --- | --- |

ii.

When there is a very intense and long rainy period, it is recommended to flush the system prior to the beginning of the next irrigation season.

7.3.4.3.   Good practice recommendations regarding the water used during harvest and post-harvest (associated operations)

| a. | Many harvest and post-harvest operations include washing, rinsing, cooling, sorting and transport of the FFVs. The water used for these associated operations is hereafter called ‘wash water’. |
| --- | --- |

a.

Many harvest and post-harvest operations include washing, rinsing, cooling, sorting and transport of the FFVs. The water used for these associated operations is hereafter called ‘wash water’.

| b. | In general, washing (by immersion or spraying) fresh produce may partly reduce the microbial load. This is an important step since most microbial contamination is on the surface of FFV. However, wash water can also redistribute the microorganisms and potentially contaminate a greater proportion of the produce. |
| --- | --- |

b.

In general, washing (by immersion or spraying) fresh produce may partly reduce the microbial load. This is an important step since most microbial contamination is on the surface of FFV. However, wash water can also redistribute the microorganisms and potentially contaminate a greater proportion of the produce.

| c. | The wash water used should be at least of clean water quality for initial washing stages. Water used for final rinses has to be of potable quality if the FFV is often consumed as ready-to-eat (e.g. tomatoes, apples, pears, young carrots, spring onions ...). Therefore, a risk assessment should be conducted according to flowchart No 2 and the tools foreseen in Annex II or Annex III can be applied for evaluation of the required quality of the wash water. |
| --- | --- |

c.

The wash water used should be at least of clean water quality for initial washing stages. Water used for final rinses has to be of potable quality if the FFV is often consumed as ready-to-eat (e.g. tomatoes, apples, pears, young carrots, spring onions ...). Therefore, a risk assessment should be conducted according to flowchart No 2 and the tools foreseen in Annex II or Annex III can be applied for evaluation of the required quality of the wash water.

| d. | If a grower intends to use processing aids in wash water with harvested produce, the grower should consult the competent authorities as the use of processing aids as a chemical decontaminant is, in general, subject to Member States’ national legislation. It is the same for washing tanks, in order to maintain the quality of the water. In case chlorine disinfectants are used, care should be taken that chlorate by-products do not cause residues in food that exceed the maximum residue levels. The following actions can reduce chlorate contamination of food:






  i. | Use of the lowest possible concentrations of chlorine disinfectants that allow achieving the desired disinfection level. |
| --- | --- | --- |

d.

If a grower intends to use processing aids in wash water with harvested produce, the grower should consult the competent authorities as the use of processing aids as a chemical decontaminant is, in general, subject to Member States’ national legislation. It is the same for washing tanks, in order to maintain the quality of the water. In case chlorine disinfectants are used, care should be taken that chlorate by-products do not cause residues in food that exceed the maximum residue levels. The following actions can reduce chlorate contamination of food:

i.

Use of the lowest possible concentrations of chlorine disinfectants that allow achieving the desired disinfection level.

| ii. | A sufficient refreshment rate of the washing water. While the active chlorine evaporates, the chlorate residues concentrate in this water. |
| --- | --- |

ii.

A sufficient refreshment rate of the washing water. While the active chlorine evaporates, the chlorate residues concentrate in this water.

| iii. | A proper storage of the disinfectants as storage exposed to light or at a high temperature already causes the degradation of chlorine disinfectants to chlorate prior to their usage. |
| --- | --- |

iii.

A proper storage of the disinfectants as storage exposed to light or at a high temperature already causes the degradation of chlorine disinfectants to chlorate prior to their usage.

| e. | Vigorous washing of produce not subject to brushing may increase the likelihood of pathogen removal. Brush washing is more effective than washing without brushes. Brushes used in brush washing should be cleaned frequently. |
| --- | --- |

e.

Vigorous washing of produce not subject to brushing may increase the likelihood of pathogen removal. Brush washing is more effective than washing without brushes. Brushes used in brush washing should be cleaned frequently.

| f. | If water is contaminated during washing and then reused, it can be a vehicle for cross-contamination. Therefore, regardless of wash method used, growers should follow good practices that ensure and maintain adequate water quality by:






  iv. | refreshing wash water with a fixed frequency (discontinuous process) |
| --- | --- | --- |

f.

If water is contaminated during washing and then reused, it can be a vehicle for cross-contamination. Therefore, regardless of wash method used, growers should follow good practices that ensure and maintain adequate water quality by:

iv.

refreshing wash water with a fixed frequency (discontinuous process)

| v. | refilling the washing equipment with a fixed volume (continuous process) |
| --- | --- |

v.

refilling the washing equipment with a fixed volume (continuous process)

| vi. | application of water treatment |
| --- | --- |

vi.

application of water treatment

| vii. | Controlled use of water disinfectant agents to avoid cross-contamination. |
| --- | --- |

vii.

Controlled use of water disinfectant agents to avoid cross-contamination.

| g. | For some operations, a series of washes may be more effective than a single wash to remove soil, debris and exudates. For example, considering using an initial wash treatment to remove the bulk of field soil from produce followed by additional washes and a final potable water rinse. |
| --- | --- |

g.

For some operations, a series of washes may be more effective than a single wash to remove soil, debris and exudates. For example, considering using an initial wash treatment to remove the bulk of field soil from produce followed by additional washes and a final potable water rinse.

| h. | Installation, routine inspection and maintenance of equipment such as backflow devices and air gaps are needed, to prevent contamination of clean water with potentially contaminated water (such as between potable water fill lines and dump tank drain lines). |
| --- | --- |

h.

Installation, routine inspection and maintenance of equipment such as backflow devices and air gaps are needed, to prevent contamination of clean water with potentially contaminated water (such as between potable water fill lines and dump tank drain lines).

7.3.4.4.   Additional good practice for leafy greens, tomatoes, melons (52)

| a. | As fresh leafy vegetables may be sprayed with small amounts of water during machine harvest or in the field container just after harvest to hydrate FFVs, potable water has to be used in processes in which there is direct contact between the water and edible portions of the leafy vegetables. |
| --- | --- |

a.

As fresh leafy vegetables may be sprayed with small amounts of water during machine harvest or in the field container just after harvest to hydrate FFVs, potable water has to be used in processes in which there is direct contact between the water and edible portions of the leafy vegetables.

| b. | Tomatoes from soil-based systems may be washed to remove dust, surface dried, sized and packed. In this case, also potable water should be used. |
| --- | --- |

b.

Tomatoes from soil-based systems may be washed to remove dust, surface dried, sized and packed. In this case, also potable water should be used.

| c. | Water is sometimes used in dump tanks to transport melons and watermelons from field containers into the packing establishment. If this is the case:






  i. | Water temperatures should be higher than the internal temperatures of melons and watermelons, so as to minimize the risk of water infiltration. |
| --- | --- | --- |

c.

Water is sometimes used in dump tanks to transport melons and watermelons from field containers into the packing establishment. If this is the case:

i.

Water temperatures should be higher than the internal temperatures of melons and watermelons, so as to minimize the risk of water infiltration.

| ii. | The time when melons/watermelons remain in dump tank water should be minimized. |
| --- | --- |

ii.

The time when melons/watermelons remain in dump tank water should be minimized.

| iii. | Where possible the microbiological quality of dump tank water should be controlled, monitored and recorded. If needed, control measures should be applied to guarantee the microbiological quality of the water. |
| --- | --- |

iii.

Where possible the microbiological quality of dump tank water should be controlled, monitored and recorded. If needed, control measures should be applied to guarantee the microbiological quality of the water.

7.3.4.5.   Good practice recommendations as regards analyses of water for agricultural use

| a. | Before commencing a water sampling strategy, it is recommended to check whether the risk assessment is still valid and the preventive measures are correctly implemented and validated. Risk assessments (see 7.3.2) should be reviewed annually. |
| --- | --- |

a.

Before commencing a water sampling strategy, it is recommended to check whether the risk assessment is still valid and the preventive measures are correctly implemented and validated. Risk assessments (see 7.3.2) should be reviewed annually.

| b. | Microbial analyses (53) of the potential water sources should be performed to determine the suitability of the water source for its use as agricultural water. |
| --- | --- |

b.

Microbial analyses (53) of the potential water sources should be performed to determine the suitability of the water source for its use as agricultural water.

| c. | Visual and smell inspections should be carried out periodically with the aim of detecting possible contamination. In case of change of visual/smell characteristics, samples should be collected for control analysis. |
| --- | --- |

c.

Visual and smell inspections should be carried out periodically with the aim of detecting possible contamination. In case of change of visual/smell characteristics, samples should be collected for control analysis.

| d. | Samples of water should be taken at the point of use. |
| --- | --- |

d.

Samples of water should be taken at the point of use.

| e. | The frequency of testing (54) of agricultural water may be reduced, provided that the results of the recommended analyses are favourable for three consecutive years and taking into account whether or not the water is vulnerable to contamination, e.g. ground water. |
| --- | --- |

e.

The frequency of testing (54) of agricultural water may be reduced, provided that the results of the recommended analyses are favourable for three consecutive years and taking into account whether or not the water is vulnerable to contamination, e.g. ground water.

| f. | Additional samples should be taken in case of events such as flooding, overflow of places where manure is stored, temporary or intermittent contamination, heavy rain, etc. These additional tests should be done just after the occurrence of the event. |
| --- | --- |

f.

Additional samples should be taken in case of events such as flooding, overflow of places where manure is stored, temporary or intermittent contamination, heavy rain, etc. These additional tests should be done just after the occurrence of the event.

| g. | If a grower repeatedly finds high levels of indicator species (i.e. indicator E.coli) in water sources when tests are carried out, the following corrective actions are recommended:






  — | Stop using the water until analysis results are favourable and if it is possible and feasible, change the source. |
| --- | --- | --- |

g.

If a grower repeatedly finds high levels of indicator species (i.e. indicator E.coli) in water sources when tests are carried out, the following corrective actions are recommended:

—

Stop using the water until analysis results are favourable and if it is possible and feasible, change the source.

| — | Alternatively treat the water before irrigation (e.g. water disinfection by ultraviolet light, reverse osmosis filtration, ozone or chlorine based disinfectants, etc....) depending on the disinfection practices in place in the Member State. |
| --- | --- |

—

Alternatively treat the water before irrigation (e.g. water disinfection by ultraviolet light, reverse osmosis filtration, ozone or chlorine based disinfectants, etc....) depending on the disinfection practices in place in the Member State.

| — | The frequency of water sampling and scope of microbial testing might be adjusted to specific situations: additional sampling should be carried out to verify presence of Salmonella spp., and pathogenic E. coli (i.e. VTEC). |
| --- | --- |

—

The frequency of water sampling and scope of microbial testing might be adjusted to specific situations: additional sampling should be carried out to verify presence of Salmonella spp., and pathogenic E. coli (i.e. VTEC).

| — | Review the current risk assessment (see 7.3.1) by focusing on potential sources of faecal contamination. |
| --- | --- |

—

Review the current risk assessment (see 7.3.1) by focusing on potential sources of faecal contamination.

| — | After implementing corrective actions, if water test is still unfavourable, and if the grower is not able to change the water source, the grower should increase the time interval between the last irrigation period and harvest and change the irrigation method to prevent water coming into contact with the edible portion of the FFV, such as drip or trickle tape. |
| --- | --- |

—

After implementing corrective actions, if water test is still unfavourable, and if the grower is not able to change the water source, the grower should increase the time interval between the last irrigation period and harvest and change the irrigation method to prevent water coming into contact with the edible portion of the FFV, such as drip or trickle tape.

7.4.   Hygiene and health status for agricultural workers

7.4.1.   General principles

All workers should be aware of the basic principles of hygiene and health, and should be informed about all the possible risks related to the contamination of the product. They should receive hygiene training appropriate to their tasks and be periodically assessed. Such training should be delivered in a language and manner to ensure understanding of the required hygienic practices.

In general unauthorised visitors should be excluded from food production and handling areas. The visitors should complete a health screening questionnaire prior to admission and, where appropriate, wear protective clothing and adhere to the staff hygiene provisions of the food business. Whenever possible, harvesting, packing and inspection processes should be designed to reduce handling.

Each grower should put in place illustrated and easy to read documentation (55) related to health status, good hygiene practices, staff training and sanitary facilities, to ensure staff, contractors and visitors are aware of, and follow GHP at all times.

7.4.2.   EU Obligations set in Regulation (EC) No 852/2004

(Annex I — Part A — II.5 (d)) ‘FBO producing or harvesting plant products are to take adequate measures, as appropriate to ensure that staff handling foodstuffs are in good health and undergo training on health risks.’

7.4.3.   Good practice recommendations

| a. | Personal effects such as jewellery, watches etc., should not be worn or brought into FFV cropping or production areas. |
| --- | --- |

a.

Personal effects such as jewellery, watches etc., should not be worn or brought into FFV cropping or production areas.

| b. | When standard practices require the use of utensils or small objects, they should be duly numbered or identified. |
| --- | --- |

b.

When standard practices require the use of utensils or small objects, they should be duly numbered or identified.

| c. | Where appropriate, the workers should wear suitable protective clothing and footwear. The use of gloves may be a useful practice, as long as they are washed or replaced frequently to avoid the spread of microorganisms. Gloves use alone is not a suitable substitute for good hand washing practices, in particular:






  — | If the gloves are reusable, they should be made of materials that are easily cleaned and disinfected, and they should be cleaned regularly and stored in a dry clean area. |
| --- | --- | --- |

c.

Where appropriate, the workers should wear suitable protective clothing and footwear. The use of gloves may be a useful practice, as long as they are washed or replaced frequently to avoid the spread of microorganisms. Gloves use alone is not a suitable substitute for good hand washing practices, in particular:

—

If the gloves are reusable, they should be made of materials that are easily cleaned and disinfected, and they should be cleaned regularly and stored in a dry clean area.

| — | If disposable gloves are used, they should be discarded when they become torn or soiled. |
| --- | --- |

—

If disposable gloves are used, they should be discarded when they become torn or soiled.

| d. | Workers who have direct contact with FFV should maintain a high degree of personal cleanliness. In general, they should properly wash and dry their hands before handling FFV (e.g. at the beginning of the harvest, during harvesting and post-harvest handling, after having eaten, after having used the toilet, etc.) or touching food contact surfaces, particularly during harvesting and postharvest handling. |
| --- | --- |

d.

Workers who have direct contact with FFV should maintain a high degree of personal cleanliness. In general, they should properly wash and dry their hands before handling FFV (e.g. at the beginning of the harvest, during harvesting and post-harvest handling, after having eaten, after having used the toilet, etc.) or touching food contact surfaces, particularly during harvesting and postharvest handling.

| e. | Workers should refrain from behaviour which could result in the contamination of FFV, for example: smoking, spitting, chewing gum or eating, or sneezing or coughing over fresh produce. |
| --- | --- |

e.

Workers should refrain from behaviour which could result in the contamination of FFV, for example: smoking, spitting, chewing gum or eating, or sneezing or coughing over fresh produce.

| f. | Any sick person should immediately report illness or symptoms of illness to the grower/line manager and must not work in contact with FFV. |
| --- | --- |

f.

Any sick person should immediately report illness or symptoms of illness to the grower/line manager and must not work in contact with FFV.

| g. | As far as possible, the hygienic and sanitary facilities should:







  — | Be located in close proximity (56) to the fields and indoor premises in a manner to encourage their use and reduce the likelihood that workers will relieve themselves in the field, and in sufficient number to accommodate personnel (e.g. 1 per 20 people) and be appropriate for both genders if the workforce contains males and females (57). |
| --- | --- | --- |

g.

As far as possible, the hygienic and sanitary facilities should:

—

Be located in close proximity (56) to the fields and indoor premises in a manner to encourage their use and reduce the likelihood that workers will relieve themselves in the field, and in sufficient number to accommodate personnel (e.g. 1 per 20 people) and be appropriate for both genders if the workforce contains males and females (57).

| — | Be of appropriate design to ensure hygienic removal of wastes and avoid contamination of growing sites, FFV or agricultural inputs (e.g. agricultural water, organic fertilisers). |
| --- | --- |

—

Be of appropriate design to ensure hygienic removal of wastes and avoid contamination of growing sites, FFV or agricultural inputs (e.g. agricultural water, organic fertilisers).

| — | Have adequate facilities for hygienic (hand) washing. |
| --- | --- |

—

Have adequate facilities for hygienic (hand) washing.

| — | Be maintained under sanitary conditions and good repair. |
| --- | --- |

—

Be maintained under sanitary conditions and good repair.

| — | Include potable running water, soap, toilet paper or equivalent, and single use paper towels or equivalent. If potable running water is not available, an alternative hand washing method should be recommended by the relevant competent authority (i.e. use of soap or disinfectant). |
| --- | --- |

—

Include potable running water, soap, toilet paper or equivalent, and single use paper towels or equivalent. If potable running water is not available, an alternative hand washing method should be recommended by the relevant competent authority (i.e. use of soap or disinfectant).

| — | Portable toilets should not be cleaned in FFV cropping areas or near irrigation water sources or conveyance systems. Growers should identify the areas where it is safe to put portable toilets. |
| --- | --- |

—

Portable toilets should not be cleaned in FFV cropping areas or near irrigation water sources or conveyance systems. Growers should identify the areas where it is safe to put portable toilets.

| h. | Training should include proper hand washing and drying procedures, toilet use and proper disposal of toilet paper or equivalent. |
| --- | --- |

h.

Training should include proper hand washing and drying procedures, toilet use and proper disposal of toilet paper or equivalent.

| i. | Hand cuts and wounds should be covered by a suitable waterproof dressing and gloves worn to cover bandages where practical. If these supplies are not available, the affected person should be reassigned to another working area where they do not handle FFV or touch food contact surfaces. |
| --- | --- |

i.

Hand cuts and wounds should be covered by a suitable waterproof dressing and gloves worn to cover bandages where practical. If these supplies are not available, the affected person should be reassigned to another working area where they do not handle FFV or touch food contact surfaces.

| j. | Areas away from the field and packing lines should be provided for workers to take breaks and eat. Workers should not take any food with them into production areas to avoid possible contamination of FFV with food allergens. |
| --- | --- |

j.

Areas away from the field and packing lines should be provided for workers to take breaks and eat. Workers should not take any food with them into production areas to avoid possible contamination of FFV with food allergens.

7.5.   Control of hygiene conditions during associated activities at farm level in addition to those described in Chapters 7.3 and 7.4

7.5.1.   General principles

Harvesting methods vary depending upon the characteristics of the product. Mechanical harvesting is a common practice for some FFV and reduces the cross-contamination events that might occur during manual harvest. But if such equipment breaks down during the harvest, or it has been poorly maintained, inadequately cleaned/disinfected, or if it damages the harvested plant, it can cause spread of microbial contamination and/or conditions that support microbial growth (i.e. damaged FFV).

FFV should be stored and transported under good hygienic conditions. Storage facilities and vehicles for transporting the harvested FFVs should be constructed in a manner that will minimise damage to FFV and prevent access by pests such as insects, rodents and birds. Design and lay-out of facilities should be such as to ensure there is no risk of microbiological, chemical or physical cross-contamination. The level of risk of cross-contamination in relation to product flow within facilities should be considered and addressed at all steps (i.e. arrival of the raw-material, prewash trimming and packaging through to storage and shipping.

7.5.2.   EU Obligations set in Regulation (EC) No 852/2004

(Annex I — Part A — II.5(a)) ‘FBO producing or harvesting plant products are to take adequate measures, as appropriate to keep clean and, where necessary after cleaning, to disinfect, in an appropriate manner, facilities, equipment, containers, crates, vehicles.’

(Annex I — Part A — II.5(b)) ‘FBO producing or harvesting plant products are to take adequate measures, as appropriate to ensure, where necessary, hygienic production, transport and storage conditions for and the cleanliness of plant products.’

(Annex I — Part A — II.5(f)) ‘FBO producing or harvesting plant products are to take adequate measures, as appropriate to store and handle wastes and hazardous substances so as to prevent contamination.’

7.5.3.   Good practice recommendations as regards harvesting and packaging operations at field or at farm level

7.5.3.1.   For all establishments

| a. | Care should be taken when packing fresh produce in the field to avoid contaminating containers by exposure to manure, animal faeces, soil or water. |
| --- | --- |

a.

Care should be taken when packing fresh produce in the field to avoid contaminating containers by exposure to manure, animal faeces, soil or water.

| b. | When padding is used with post-harvest handling equipment to prevent damage, it should be constructed of material that can be cleaned and if possible disinfected. |
| --- | --- |

b.

When padding is used with post-harvest handling equipment to prevent damage, it should be constructed of material that can be cleaned and if possible disinfected.

| c. | Growers should remove excessive dirt and caked mud from produce and/or containers during harvest and should clean all their tools/utensils and containers used repeatedly during harvest after each load. |
| --- | --- |

c.

Growers should remove excessive dirt and caked mud from produce and/or containers during harvest and should clean all their tools/utensils and containers used repeatedly during harvest after each load.

| d. | Growers should avoid setting harvesting containers or harvested fresh produce directly on soil during/after harvest and before loading into transport vehicle. They should avoid using harvesting containers that come into direct contact with fresh produce for purposes other than holding produce. |
| --- | --- |

d.

Growers should avoid setting harvesting containers or harvested fresh produce directly on soil during/after harvest and before loading into transport vehicle. They should avoid using harvesting containers that come into direct contact with fresh produce for purposes other than holding produce.

| e. | Packaged products intended for direct consumption should be correctly labelled and stored. Where necessary, suitable temperature and relative humidity conditions should be fixed for storage. |
| --- | --- |

e.

Packaged products intended for direct consumption should be correctly labelled and stored. Where necessary, suitable temperature and relative humidity conditions should be fixed for storage.

| f. | Growers should avoid over-filling totes and bins to prevent the potential transfer of contaminants to fresh produce during stacking. It would also prevent damage to the produce. |
| --- | --- |

f.

Growers should avoid over-filling totes and bins to prevent the potential transfer of contaminants to fresh produce during stacking. It would also prevent damage to the produce.

| g. | Clean cuts should be made to harvested fruit and vegetables, without tearing the stem or stalk. |
| --- | --- |

g.

Clean cuts should be made to harvested fruit and vegetables, without tearing the stem or stalk.

| h. | Any leftover packaging material and culled FFV should be taken away from the field at the end of the day |
| --- | --- |

h.

Any leftover packaging material and culled FFV should be taken away from the field at the end of the day

| i. | FFV unfit for human consumption should be left un-harvested or segregated during harvesting. |
| --- | --- |

i.

FFV unfit for human consumption should be left un-harvested or segregated during harvesting.

| j. | Culls should be hygienically removed from the packing facility by a worker who is not handling healthy fruit or vegetables and disposed of to avoid attracting pests. |
| --- | --- |

j.

Culls should be hygienically removed from the packing facility by a worker who is not handling healthy fruit or vegetables and disposed of to avoid attracting pests.

7.5.3.2.   Additional specific good practice recommendations for growers of tomatoes, berries, melons and watermelons

| a. | Where materials are used during growing of berries, tomatoes, melons/watermelons under them to minimize contact with the soil (e.g. mulch or biodegradable materials such as straw), or during harvest to protect collected fruit (e.g. plastic or biodegradable materials such as leaves or paper liners or any kind of biodegradable baskets):






  — | Plastic should be clean and sanitary. |
| --- | --- | --- |

a.

Where materials are used during growing of berries, tomatoes, melons/watermelons under them to minimize contact with the soil (e.g. mulch or biodegradable materials such as straw), or during harvest to protect collected fruit (e.g. plastic or biodegradable materials such as leaves or paper liners or any kind of biodegradable baskets):

—

Plastic should be clean and sanitary.

| — | Biodegradable materials and/or mulch should not be reused in order to prevent cross contamination. |
| --- | --- |

—

Biodegradable materials and/or mulch should not be reused in order to prevent cross contamination.

| b. | Good hygienic practices should be maintained along the food chain, as berries are mainly consumed raw and/or subjected to minimal processing such as cleaning, washing or cooling. |
| --- | --- |

b.

Good hygienic practices should be maintained along the food chain, as berries are mainly consumed raw and/or subjected to minimal processing such as cleaning, washing or cooling.

| c. | Berries should be cooled immediately after harvesting. When required, growers should use potable water for ice and hydro coolers when precooling to minimise risks of contamination. |
| --- | --- |

c.

Berries should be cooled immediately after harvesting. When required, growers should use potable water for ice and hydro coolers when precooling to minimise risks of contamination.

| d. | In the case of hand harvesting, growers should consider the following guidance:






  — | Appearance and firmness of berries are commonly associated with fruit quality and freshness. Over-handling the berries may damage them and affect fruit quality. Moreover, adverse temperatures during harvesting in hot and/or humid weather also decreases quality and may affect food safety due to fruit damage and juice leakage, which may spread contamination over healthy fruits. |
| --- | --- | --- |

d.

In the case of hand harvesting, growers should consider the following guidance:

—

Appearance and firmness of berries are commonly associated with fruit quality and freshness. Over-handling the berries may damage them and affect fruit quality. Moreover, adverse temperatures during harvesting in hot and/or humid weather also decreases quality and may affect food safety due to fruit damage and juice leakage, which may spread contamination over healthy fruits.

| — | Growers are encouraged to designate a responsible person to supervise harvesting at all times to ensure harvesters use proper hand washing procedures and to avoid harvesting wet, bruised and/or damaged fruits. |
| --- | --- |

—

Growers are encouraged to designate a responsible person to supervise harvesting at all times to ensure harvesters use proper hand washing procedures and to avoid harvesting wet, bruised and/or damaged fruits.

| e. | Some growers place melons and watermelons on cups (i.e. small plastic pads), plastic mulch-covered beds or halved bamboo segments to minimize direct melon-to-soil contact and thereby reduce ground spot development. They may also be hand-turned multiple times by workers during the growing season to prevent sunburn or ground spot development, or covered with biodegradable materials such as rice straw to prevent sunburn. When cups or biodegradable materials are used the following practices are recommended:






  — | Before setting cups underneath melons/watermelons, ensure that they are clean, sanitary, without sharp edges and do not result in water collection under the fruit surface. |
| --- | --- | --- |

e.

Some growers place melons and watermelons on cups (i.e. small plastic pads), plastic mulch-covered beds or halved bamboo segments to minimize direct melon-to-soil contact and thereby reduce ground spot development. They may also be hand-turned multiple times by workers during the growing season to prevent sunburn or ground spot development, or covered with biodegradable materials such as rice straw to prevent sunburn. When cups or biodegradable materials are used the following practices are recommended:

—

Before setting cups underneath melons/watermelons, ensure that they are clean, sanitary, without sharp edges and do not result in water collection under the fruit surface.

| — | When turning melons/watermelons on the cups and during harvesting operations ensure that workers follow good hygienic practices. |
| --- | --- |

—

When turning melons/watermelons on the cups and during harvesting operations ensure that workers follow good hygienic practices.

| — | Use biodegradable materials only once to prevent cross-contamination. |
| --- | --- |

—

Use biodegradable materials only once to prevent cross-contamination.

7.5.4.   Good practice recommendations as regards operations of loading/transport/storage and cleaning/disinfection operations

7.5.4.1.   At farm, packing and transport level

| a. | Products should be loaded in such a way that they do not suffer any damage during transport. |
| --- | --- |

a.

Products should be loaded in such a way that they do not suffer any damage during transport.

| b. | All efforts should be made to protect the harvested products from the sun, the wind, the rain, pests and other animals. |
| --- | --- |

b.

All efforts should be made to protect the harvested products from the sun, the wind, the rain, pests and other animals.

| c. | The harvested products should be taken to the handling and packing area as quickly as possible. Where the temperature is high, the transfer should be accelerated. |
| --- | --- |

c.

The harvested products should be taken to the handling and packing area as quickly as possible. Where the temperature is high, the transfer should be accelerated.

| d. | The product may be placed in field boxes or other containers suitable for food use, without throwing or pressing. Boxes should not be filled above their top edges. |
| --- | --- |

d.

The product may be placed in field boxes or other containers suitable for food use, without throwing or pressing. Boxes should not be filled above their top edges.

| e. | Storage areas are clean and suitable for each type of product stored. Harvested products must not be stored together with potential sources of contamination, e.g. animals, chemical products etc. |
| --- | --- |

e.

Storage areas are clean and suitable for each type of product stored. Harvested products must not be stored together with potential sources of contamination, e.g. animals, chemical products etc.

| f. | The vehicles for transport should be clean: FFV should not be transported together with potential sources of contamination, e.g. animals, chemical products. If the vehicle has been previously used to transport animals, plant protection products, biocides, engine lubricant, fuel or any waste material, the vehicles should be suitably cleaned, and if necessary disinfected, before being used to transport FFV. In all cases vehicles used to transport FFV should be periodically cleaned. |
| --- | --- |

f.

The vehicles for transport should be clean: FFV should not be transported together with potential sources of contamination, e.g. animals, chemical products. If the vehicle has been previously used to transport animals, plant protection products, biocides, engine lubricant, fuel or any waste material, the vehicles should be suitably cleaned, and if necessary disinfected, before being used to transport FFV. In all cases vehicles used to transport FFV should be periodically cleaned.

| g. | FFV unfit for human consumption should be separated before storage or transport. Those which cannot be made safe by further processing should be disposed of hygienically. |
| --- | --- |

g.

FFV unfit for human consumption should be separated before storage or transport. Those which cannot be made safe by further processing should be disposed of hygienically.

7.5.4.2.   Cleaning, maintenance and disinfection operations

| a. | The field boxes or other containers used for the transport of FFV should be cleaned periodically and should not have any cracks or protrusions that could damage the product. |
| --- | --- |

a.

The field boxes or other containers used for the transport of FFV should be cleaned periodically and should not have any cracks or protrusions that could damage the product.

| b. | Cleaning procedures should include the removal of debris from equipment surfaces, application of a detergent solution, rinsing with water, and, where appropriate, disinfection. |
| --- | --- |

b.

Cleaning procedures should include the removal of debris from equipment surfaces, application of a detergent solution, rinsing with water, and, where appropriate, disinfection.

| c. | The effectiveness of cleaning and disinfection of food contact surfaces should be periodically verified by swabbing. |
| --- | --- |

c.

The effectiveness of cleaning and disinfection of food contact surfaces should be periodically verified by swabbing.

| d. | Where appropriate, an adequate supply of clean water with appropriate facilities for its storage and distribution should be available in indoor primary production facilities. |
| --- | --- |

d.

Where appropriate, an adequate supply of clean water with appropriate facilities for its storage and distribution should be available in indoor primary production facilities.

| e. | Clean water should be used to clean all equipment directly contacting FFV, including farm machinery, harvesting and transportation equipment, containers and knives. |
| --- | --- |

e.

Clean water should be used to clean all equipment directly contacting FFV, including farm machinery, harvesting and transportation equipment, containers and knives.

| f. | Non-potable water should have a separate system. Non potable water systems should be clearly identified and should not connect with, or allow reflux into, potable water systems. |
| --- | --- |

f.

Non-potable water should have a separate system. Non potable water systems should be clearly identified and should not connect with, or allow reflux into, potable water systems.

| g. | Adequate drainage and waste disposal systems and facilities should be provided. |
| --- | --- |

g.

Adequate drainage and waste disposal systems and facilities should be provided.

| h. | Growers should properly store their equipment, and cut weeds or grass within the immediate vicinity of the buildings. |
| --- | --- |

h.

Growers should properly store their equipment, and cut weeds or grass within the immediate vicinity of the buildings.

| i. | Growers should avoid moving harvesting equipment across fields where manure or compost was applied. |
| --- | --- |

i.

Growers should avoid moving harvesting equipment across fields where manure or compost was applied.

| j. | Growers are recommended to clean and disinfect harvesting equipment seasonally or as needed. |
| --- | --- |

j.

Growers are recommended to clean and disinfect harvesting equipment seasonally or as needed.

| k. | A schedule for the cleaning and disinfection of these facilities, as well as the equipment and utensils used for packaging is recommended. |
| --- | --- |

k.

A schedule for the cleaning and disinfection of these facilities, as well as the equipment and utensils used for packaging is recommended.

| l. | Cleaning and disinfection programmes should not be carried out in a location where the rinse might contaminate FFV. |
| --- | --- |

l.

Cleaning and disinfection programmes should not be carried out in a location where the rinse might contaminate FFV.

| m. | A grower can use biocides to disinfect the food contact surfaces, equipment used for washing, rinsing and cooling of FFV. |
| --- | --- |

m.

A grower can use biocides to disinfect the food contact surfaces, equipment used for washing, rinsing and cooling of FFV.

| n. | Cleaning materials (e.g. detergents, biocides, etc.) should be clearly identifiable and kept separately in secure and good storage facilities (58). They should be properly authorized and used for their intended purpose according to the manufacturer’s instructions. |
| --- | --- |

n.

Cleaning materials (e.g. detergents, biocides, etc.) should be clearly identifiable and kept separately in secure and good storage facilities (58). They should be properly authorized and used for their intended purpose according to the manufacturer’s instructions.

7.5.4.3.   Additional good practice recommendations in relation to storage and packing facilities for growers of tomatoes, berries, melons/watermelons and leafy greens.

| a. | In general, but especially for tomatoes, melons and watermelons, those that have undergone cleaning and/or chemical treatment should be effectively separated, i.e. in separate premises or treated at separate times, from raw material and environmental contaminants. In addition, packing premises and rooms should be designed to separate areas for incoming tomatoes from the field (areas for incoming soiled tomatoes) from those used for subsequent handling. Where feasible, raw material handling areas should be separated from packing areas. |
| --- | --- |

a.

In general, but especially for tomatoes, melons and watermelons, those that have undergone cleaning and/or chemical treatment should be effectively separated, i.e. in separate premises or treated at separate times, from raw material and environmental contaminants. In addition, packing premises and rooms should be designed to separate areas for incoming tomatoes from the field (areas for incoming soiled tomatoes) from those used for subsequent handling. Where feasible, raw material handling areas should be separated from packing areas.

| b. | During cooling and washing of leafy greens, maintenance of the microbial quality either by sufficient water renewal or by water treatment should be ensured to reduce the build-up of microorganisms and reduce risks of cross-contamination of produce. |
| --- | --- |

b.

During cooling and washing of leafy greens, maintenance of the microbial quality either by sufficient water renewal or by water treatment should be ensured to reduce the build-up of microorganisms and reduce risks of cross-contamination of produce.

8.   RECORD KEEPING AND RESPONSIBILITIES FOR FOOD RECALLS/WITHDRAWALS

8.1.   Record keeping

8.1.1.   General principles

An effective traceability system (back and forward) should be documented to indicate the source of a product and a mechanism for marking or identifying the product that can trace the product from the farm. The grower may be assisted by other persons, such as farm technicians, with the keeping of records.

This information should be made available to the competent authorities on request, as well as the food business operators taking delivery of the harvested products.

8.1.2.   EU Obligations set in Regulation (EC) No 852/2004

(Annex I — Part A — III. 7): Food business growers are to keep and retain records relating to measures put in place to control hazards in an appropriate manner and for an appropriate period, commensurate with the nature and size of the food business. Food business growers are to make relevant information contained in these records available to the competent authority and receiving food business growers on request.

(Annex I — Part A — III. 9 (a) to (c)): Food business operators producing or harvesting plant products have, in particular, to keep records on:

| a) | Any use of plant protection products and biocides, |
| --- | --- |

a)

Any use of plant protection products and biocides,

| b) | Any occurrence of pests or diseases that may affect the safety of products of plant origin, |
| --- | --- |

b)

Any occurrence of pests or diseases that may affect the safety of products of plant origin,

| c) | The results of any relevant analyses carried out on samples taken from FFVs or other samples that have importance to human health. |
| --- | --- |

c)

The results of any relevant analyses carried out on samples taken from FFVs or other samples that have importance to human health.

8.1.3.   Good practice recommendations

| a. | Detailed records that link each supplier of the product involved in the primary production supply chain should be kept, including the following type of records:






  — | Identification of the farm and place of production (e.g. field name/poly tunnel/growing room....) |
| --- | --- | --- |

a.

Detailed records that link each supplier of the product involved in the primary production supply chain should be kept, including the following type of records:

—

Identification of the farm and place of production (e.g. field name/poly tunnel/growing room....)

| — | Type of product (e.g. fruit or vegetable name and/or variety name etc.) |
| --- | --- |

—

Type of product (e.g. fruit or vegetable name and/or variety name etc.)

| — | Source of seed/plants for propagation |
| --- | --- |

—

Source of seed/plants for propagation

| — | Date of planting of harvest and method of harvesting |
| --- | --- |

—

Date of planting of harvest and method of harvesting

| — | Source of irrigation and method |
| --- | --- |

—

Source of irrigation and method

| — | Last date of irrigation before FFV harvest |
| --- | --- |

—

Last date of irrigation before FFV harvest

| — | FFV inputs (fertiliser, plant protection products, date, doses, ...) |
| --- | --- |

—

FFV inputs (fertiliser, plant protection products, date, doses, ...)

| — | Date of packing and release |
| --- | --- |

—

Date of packing and release

| — | Batch identification |
| --- | --- |

—

Batch identification

| — | Transport identification |
| --- | --- |

—

Transport identification

| — | Storage room temperature levels |
| --- | --- |

—

Storage room temperature levels

| — | Employee training records, Equipment monitoring and maintenance records |
| --- | --- |

—

Employee training records, Equipment monitoring and maintenance records

| — | Cleaning and disinfection reports for buildings/structures and equipment |
| --- | --- |

—

Cleaning and disinfection reports for buildings/structures and equipment

| — | Results of microbiological tests carried out to verify the effectiveness of cleaning and disinfection of food contact surfaces and equipment |
| --- | --- |

—

Results of microbiological tests carried out to verify the effectiveness of cleaning and disinfection of food contact surfaces and equipment

| — | Inspection/audit records. |
| --- | --- |

—

Inspection/audit records.

| b. | It is recommended to keep records for at least 3 years. Measures put in place to control hazards in FFV production (see previous sections of the document for the controls recommended), e.g. bacterial pathogens or chemical contaminants should be recorded. Controls put in place should be documented for:






  — | Water used for both irrigation, application of plant protection products and fertilisers, washing of food and equipment, personal hygiene |
| --- | --- | --- |

b.

It is recommended to keep records for at least 3 years. Measures put in place to control hazards in FFV production (see previous sections of the document for the controls recommended), e.g. bacterial pathogens or chemical contaminants should be recorded. Controls put in place should be documented for:

—

Water used for both irrigation, application of plant protection products and fertilisers, washing of food and equipment, personal hygiene

| — | Organic fertilisers |
| --- | --- |

—

Organic fertilisers

| — | Waste material |
| --- | --- |

—

Waste material

| — | Personnel — training to show personnel are aware of hazards, return to work after illness procedures. |
| --- | --- |

—

Personnel — training to show personnel are aware of hazards, return to work after illness procedures.

8.2.   Responsibilities for food recalls/withdrawals

8.2.1.   EU Obligations set in Regulation (EC) No 178/2002 — Articles 14, 18, 19

(Article 14(1)) ‘Food shall not be placed on the market if it is unsafe.’

(Articles 14(2) and (6)) Unsafe food is defined as ‘food that is injurious to health and/or unfit for human consumption’ and ‘Where any food which is unsafe is part of a batch, lot or consignment of food of the same class or description, it shall be presumed that all the food in that batch, lot or consignment is also unsafe, unless following a detailed assessment there is no evidence that the rest of the batch, lot or consignment is unsafe.’

(Article 18(2)) ‘Food business operators shall be able to identify any person from whom they have been supplied with a food or any substance intended to be, or expected to be, incorporated into a food (...). To this end, such operators shall have in place systems and procedures which allow for this information to be made available to the competent authorities on demand’.

(Article 18(3)) ‘Food business operators shall have in place systems and procedures to identify the other businesses to which their products have been supplied. This information shall be made available to the competent authorities on demand.’

(Article 18(4)) ‘Food which is placed on the market or is likely to be placed on the market in the Community shall be adequately labelled or identified to facilitate its traceability, through relevant documentation or information in accordance with the relevant requirements of more specific provisions’.

(Article 19(1)) ‘If a food business operator considers or has reason to believe that a food which it has imported, produced, processed, manufactured or distributed is not in compliance with the food safety requirements, it shall immediately initiate procedures to withdraw the food in question from the market where the food has left the immediate control of that initial food business operator and inform the competent authorities thereof. Where the product may have reached the consumer, the operator shall effectively and accurately inform the consumers of the reason for its withdrawal, and if necessary, recall from consumers products already supplied to them when other measures are not sufficient to achieve a high level of health protection’.

(Article 19(3)) ‘A food business operator shall immediately inform the competent authorities if it considers or has reason to believe that a food which it has placed on the market may be injurious to human health. Growers shall inform the competent authorities of the action taken to prevent risks to the final consumer and shall not prevent or discourage any person from cooperating, in accordance with national law and legal practice, with the competent authorities, where this may prevent, reduce or eliminate a risk arising from a food.’

(Article 19(4)) ‘Food business operators shall collaborate with the competent authorities on action taken to avoid or reduce risks posed by a food which they supply or have supplied.’

8.2.2.   Good practice recommendations

| a. | A food recall/withdrawal plan consists of a set of documents/support materials designed to facilitate the removal of food from the market and to provide the correct information to businesses, consumers and the competent authorities. |
| --- | --- |

a.

A food recall/withdrawal plan consists of a set of documents/support materials designed to facilitate the removal of food from the market and to provide the correct information to businesses, consumers and the competent authorities.

| b. | The grower should ensure that the recalled food is not placed on the market through other channels. |
| --- | --- |

b.

The grower should ensure that the recalled food is not placed on the market through other channels.

| c. | In the event of a foodborne illness outbreak associated with FFV, maintaining appropriate records of production and associated operations such as packaging and transport may help identify the source of contamination in the food chain and facilitate product recalls. |
| --- | --- |

c.

In the event of a foodborne illness outbreak associated with FFV, maintaining appropriate records of production and associated operations such as packaging and transport may help identify the source of contamination in the food chain and facilitate product recalls.

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(1)  The European Union summary report on trends and sources of zoonoses, zoonotic agents and food-borne outbreaks in 2014, http://onlinelibrary.wiley.com/doi/10.2903/j.efsa.2015.4329/pdf

(2)  http://ec.europa.eu/dgs/health_consumer/dyna/consumervoice/create_cv.cfm?cv_id=740

(3)  As follow up of this EFSA Opinion, 4 specific regulations have been adopted: Commission Regulations (EU) No 208/2013, (EU) No 209/2013, (EU) No 210/2013 and (EU) No 211/2013 of 11 March 2013 on traceability requirements, on approval, on microbiological criteria, and on certification requirements for imports into the Union of sprouts and seeds intended for the production of sprouts.

(4)  For example, modified atmosphere packaging, or peeling or shredding to smaller pieces used for fresh minimally processed fruits and vegetables are not within scope of Annex I.

(5)  Mycotoxins are excluded from the scope of this guide, as it is based on EFSA opinions related to microbiological pathogens.

(6)  Leafy greens eaten raw as salads, berries, tomatoes, melons and bulbs/stem vegetables and carrots.

(7)  See definition of sprouts in Article 2 of Commission Implementing Regulation (EU) No 208/2013 on traceability requirements for sprouts and seeds intended for the production of sprouts. Sprouted seeds fall under the scope of Annex I of Reg. 852/2004 (Primary production) (OJ L 139, 30.4.2004, p. 1).

(8)  OJ L 31, 1.2.2002, p. 1.

(9)  OJ L 139, 30.4.2004, p. 1.

(10)  OJ L 338, 22.12.2005, p. 1.

(11)  OJ L 70, 16.3.2005, p. 1.

(12)  OJ L 181, 4.7.1986, p. 6.

(13)  OJ L 330, 5.12.1998, p. 32.

(14)  OJ L 375, 31.12.1991, p. 1.

(15)  OJ L 300, 14.11.2009, p. 1.

(16)  OJ L 54, 26.2.2011, p. 1.

(17)  DK/HU/PT/RO/SK.

(18)  CAC/GL 79-2012, CAC/RCP 53-2003, CAC/RCP 42-1995, and CAC/RCP 1-1969:

http://www.codexalimentarius.org/standards/list-standards/en/?no_cache=1?provide=standards&orderField=ccshort&sort=asc&num1

(19)  NB: If inorganic fertilisers are used, no need to answer the other questions of this check list as they are not described in this guide.

(20)  Regulation (EC) No 1069/2009 of the European Parliament and of the Council of 21 October 2009 laying down health rules as regards animal by-products and derived products not intended for human consumption and repealing Regulation (EC) No 1774/2002 (OJ L 300, 14.11.2009, p. 1).

(21)  Council Directive 86/278/EEC of 12 June 1986 on the protection of the environment, and in particular of the soil, when sewage sludge is used in agriculture (OJ L 181, 4.7.1986, p. 6).

(22)  As described in Chapter 7.4 (paragraph 7.4.3).

(23)  As described in paragraph 7.5.4.2.

(24)  Regulation (EC) No 1107/2009 of the European Parliament and of the Council of 21 October 2009 concerning the placing of plant protection products on the market and repealing Council Directives 79/117/EEC and 91/414/EEC (OJ L 309, 24.11.2009, p. 1).

(25)  In line within the requirements of Integrated Pest Management.

(26)  Only edible part is considered here.

(27)  Although this guide deals with organic fertilisers only, the risks associated with using water soluble inorganic fertilisers are covered in the section on water (Chapter 7.3 of the guide).

(28)  Commission Regulation (EU) No 142/2011 of 25 February 2011 implementing Regulation (EC) No 1069/2009 of the European Parliament and of the Council laying down health rules as regards animal by-products and derived products not intended for human consumption and implementing Council Directive 97/78/EC as regards certain samples and items exempt from veterinary checks at the border under that Directive lays down requirements for transformation of animal by-products in the production of organic fertilisers and soil improvers, including some microbiological standards for digestion residues and compost. Manure produced and used on the same farm may be applied to land without processing if the competent authority does not consider it to be a risk for the transmission of any serious transmissible disease (OJ L 54, 26.2.2011, p. 1).

(29)  I.e. a plan for spreading livestock manure, slurries and organic wastes on the farm. Any plan will help the grower to minimise the risk of causing water pollution. This plan should help to meet national legislative requirements transposing Council Directive 91/676/EEC.

(30)  To protect water against pollution caused by nitrates, the spreading time of treated manures must be done respecting the requirements established by Council Directive 91/676/EEC.

(31)  According to ‘EFSA’s scientific opinion on the risk from Salmonella and Norovirus in leafy greens eaten raw as salads reports’.

(32)  Conventional treated sewage sludge includes lagoon stored, thickened and mesophilic anaerobic digested sludge. Treatment must ensure 99 % of pathogens have been destroyed (a 2 log reduction).

(33)  Enhanced treated sewage sludge includes pasteurisation, thermophilic digestion, lime stabilisation and composting. Treatment must ensure 99,9999 % of pathogens have been destroyed (a 6 log reduction).

(34)  Commission Regulation (EU) No 142/2011 lays down some microbiological standards for digestion residues and compost derived from processing of Animal By-Products, including manure.

(*1)  These pre-harvest intervals are examples of good practice and growers should interpret this guidance according to the risks associated with their particular operation. Factors that affect the rate at which pathogens in fresh manures/slurry die off after application to land include temperature, UV radiation, pH, drying, soil type etc. Other time periods may therefore be justified based on regional differences in climate and environmental conditions etc.

(1)  Where livestock grazing is an essential part of the farming system (e.g. in some organic farms) there should be a minimum 6 months gap between livestock grazing and harvest. To minimise risks further, the guidance in the table above should be followed where practically possible.

(35)  For example BSi PAS 110 or equivalent.

(36)  For example BSi PAS 100 or equivalent.

(37)  Farm manures and slurry should be stored as a batch for a minimum of six months with no additions of fresh manure or slurry during this time. More active forms of treatment include composting (solid manures) and lime treatment (slurry) (see Section 7.2.3.2).

(38)  Conventional treated sewage sludge includes lagoon stored, thickened and mesophilic anaerobic digested sludge. Treatment must ensure 99 % of pathogens have been destroyed (a 2 log reduction).

(39)  Enhanced treated sewage sludge includes pasteurisation, thermophilic digestion, lime stabilisation and composting. Treatment must ensure 99,9999 % of pathogens have been destroyed (a 6 log reduction).

(40)  May have history of pathogen contamination, e.g. whole head lettuce, leafy salads, celery, salad onions, radish, fresh and frozen herbs, etc.

(41)  Target of zero and absolute limit of < 0,1 % (m/m dry weight) glass must be achieved (i.e. limit for glass debris/contamination of the compost or treated manure).

(42)  May have history of pathogen contamination, e.g. apple, beetroot, blackcurrant, blueberry, broad bean, broccoli, cabbage, capsicum, carrot, cauliflower, celeriac, cherry, courgette, cucumber, garlic, green beans (other than runner beans), melon, mushroom, onion (red and white), pea, pear, peach, plum, raspberry, strawberry, sugar snap peas, sweet corn, tomato and tree nuts, etc.

(43)  Target of zero and absolute limit of < 0,1 % (m/m dry weight) glass must be achieved (i.e. limit for glass debris/contamination of the compost or treated manure).

(44)  For example artichoke, leek, marrow, parsnip, potato, pumpkin, runner bean, squash, swede, turnip, etc.

(45)  ISO 16075-2:2015 Guidelines for treated wastewater use for irrigation projects.

(46)  http://www.fao.org/DOCReP/003/T0234e/T0234e00.htm; ftp://ftp.fao.org/docrep/fao/010/a1336e/a1336e07.pdf

(47)  http://apps.who.int/iris/bitstream/10665/78265/1/9241546824_eng.pdf

(48)  When multiple sources or a mixture of water of different sources are applied, conduct the risk assessment for each source used.

(49)  (The definition of processing aids in FFV is harmonised within the EU (Regulation (EC) No 1333/2008), and disinfecting agents have to be approved according to the Regulation (EU) No 528/2012 of the European Parliament and of the Council of 22 May 2012 (OJ L 167, 27.6.2012, p. 1) concerning the making available on the market and use of biocidal products. Substances used as processing aids shall be used under conditions of good manufacturing practices (GMP). Some companies use chlorine or other agents to control microbial load in the water. Chlorine in the form of sodium hypochlorite granules, tablets or liquid is the most commonly used as disinfection agent. The quantities of chlorine used should be compatible with the EU maximum level of chlorates that could be found in the final product (see also point 7.3.4.3(d)). In addition, Chlorate is a substance that is no longer approved as a pesticide according to Commission Decision No 2008/865/EC. Since no specific MRL was fixed under Regulation (EC) No 396/2005 on maximum residue levels for pesticides, the default MRL of 0,01 mg/kg is applicable to all food products included in Annex I to that Regulation. The MRLs of Regulation (EC) No 396/2005 are applicable to residues of substances that are currently used or have been formerly used as pesticides. The MRL of 0,01 mg/kg is therefore applicable to chlorate even though most of the current residues arise from uses of chlorine disinfectants as biocides).

(50)  It is the same for pesticides application.

(51)  If the quality of water is not very high, this method of irrigation should only be used during the early stages of growth.

(52)  Categories of fruits and Vegetables evaluated by EFSA Opinions as the most risky categories: produce contaminated by Salmonella/Noroviruses.

(53)  Water samples should be sent to a laboratory for microbial analyses.

(54)  If it is decided to include the proposed microbiological testing frequencies, see the frequencies set up in Annex II, pages 35 to 37.

(55)  Documentation means posters on walls, or leaflets left in visible places, where they can be seen by anyone who enters the establishment.

(56)  E.g. max. 400 m or 5 minutes walking distance.

(57)  E.g. if there are less than 25 workers, one mixed toilet is allowed. If there are more than 25 workers, there should be one toilet for every 20 workers, and separated by gender.

(58)  For example hypochlorites which are not correctly stored may be transformed into an accumulation of chlorates.

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ANNEX I

GLOSSARY

The definitions laid down in Regulations (EC) No 178/2002, (EC) No 852/2004, (EC) No 2073/2005, Council Directive 86/278/EEC apply and are underlined. For the purpose of this guidance document, the following terms are defined as below:

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| i. | Sorting, removing outer leaves, washing/rinsing, packing, cooling, transport, storage and handling of primary products at the place of production, provided that this does not substantially alter their nature; |
| --- | --- |

i.

Sorting, removing outer leaves, washing/rinsing, packing, cooling, transport, storage and handling of primary products at the place of production, provided that this does not substantially alter their nature;

| ii. | The term ‘primary production’ in this guidance document should be understood as primary production including these associated operations. |
| --- | --- |

ii.

The term ‘primary production’ in this guidance document should be understood as primary production including these associated operations.

| iii. | The harvesting of wild mushrooms, seaweed and berries and their transport to an establishment. |
| --- | --- |

iii.

The harvesting of wild mushrooms, seaweed and berries and their transport to an establishment.

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(1)  Committee on agriculture — Seventeenth Session — Rome, 31 March-4 April 2003-Development of a Framework for Good Agricultural Practices — http://www.fao.org/docrep/meeting/006/y8704e.htm

(2)  Regulation (EC) No 1333/2008 of the European Parliament and of the Council of 16 December 2008 on food additives (OJ L 354, 31.12.2008, p. 16).

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ANNEX II

EXAMPLE OF MATRIX TO SUPPORT MICROBIOLOGICAL RISK ASSESSMENT OF AGRICULTURAL WATER

This matrix provides growers with a tool to perform a risk assessment of water used in primary agricultural production due to the combination of water source, irrigation method or potential contact with FFVs and commodity type (ready-to-eat or not).

It sets frequencies (high, medium and low) for analysis of the water for indicators of faecal contamination (indicator E. coli) during the use of the water (growing season or period of application of the water source) and corresponding thresholds, depending on the intended use of the water, the water source, the characteristic and the nature of the FFV.

High frequency would correspond to one analysis per month; medium frequency one analysis twice a year and low frequency once per year. But in any case, the scheme and recommended measures are just examples, which may be modified, based on the risk assessment of each farm. A year can be defined as a calendar year in case of year-round production (e.g. greenhouses) or can be the growth season.

This matrix suggests that the grower should take a number of samples, larger on higher risk FFVs that are eaten uncooked by the consumer and actions to reduce the risk of contamination of FFV are proposed. In case of irrigation, the samples should be taken during peak-use period for irrigation and if there are crops in summer, at least, one of the samples should be taken in this season.

If the test result of the water source is unfavourable or identifies a potential problem, the grower should take some corrective actions set out in points 7.3.4.1 and 7.3.4.2, to reduce the risk to the consumer and after that, another water test should be carried out, to verify the effectiveness of the actions taken.

The meaning of the signs’ code and the numbers are the following (Water source):

x Dark Grey: should not be used. If the grower has no alternative but to use it, he should carry out high frequency testing or consider water treatment/disinfection, taking E. coli thresholds in column 8, as a meaningful indicator for an acceptable quality water to use in that activity.

Image
Medium-Dark Grey: can be used, but subject to sampling. The grower should carry out testing with medium frequency, taking E. coli thresholds in column 8, as a meaningful indicator for an acceptable quality water to use in that activity.

Image Light Grey: can be used, but subject to sampling. The grower should carry out testing with low frequency, taking E. coli thresholds in column 8, as a meaningful indicator for an acceptable quality water to use in that activity.

√ White: can be used without any sampling or analysis, or with only analysis required, to monitor the disinfection of water.

| Intended use of the water | Source of water
   (1) | Indicator of faecal contamination: E. coli
   (2) |
| --- | --- | --- |
| Untreated
  surface water/open water channels (3) | Untreated ground water collected from wells (4) | Untreated
  Rain water | Treated (5) sewage/surface/waste water/water reuse | Disinfected water (6) | Municipal water |
| PRE-HARVEST and HARVEST |
| Irrigation of FFVs likely to be eaten uncooked (i.e. ready-to-eat FFV) (irrigation water comes into direct contact with the edible portion of the FFV)
  Dilution or application of pesticide, fertiliser or agrochemicals and cleaning equipment for ready-to-eat FFV and direct contact. | x | x | | | | √ | 100 CFU/100 ml |
| Irrigation of FFVs likely to be eaten uncooked (i.e. ready-to-eat FFV) (irrigation water does not come into direct contact with the edible portion of the FFV)
  Dilution or application of pesticide, fertiliser or agrochemicals and cleaning equipment for ready-to-eat FFV and no direct contact | x | x | | | | √ | 1 000 CFU/100 ml (7) |
| Irrigation of FFVs likely to be eaten cooked (irrigation water comes into direct contact with the edible portion of the FFV).
  Dilution or application of pesticide, fertiliser or agrochemicals and cleaning equipment used in this FFV direct contact). | | | | | | √ | 1 000 CFU/100 ml |
| Irrigation of FFVs likely to be eaten cooked (irrigation water does not come into direct contact with the edible portion of the FFV).
  Dilution or application of pesticide, fertiliser or agrochemicals and cleaning equipment used in this FFV (no direct contact) | | | √ | √ | √ | √ | 10 000 CFU/100 ml |
| POST-HARVEST |
| Post-harvest cooling and post-harvest transport for non-ready-to-eat FFVs.
  Water used for first washing of products in case of ready-to-eat products.
  Cleaning equipment and surfaces where the products are handled. | x | x | | | | √ | 100 CFU/100 ml |
| Water used for washing of products likely to be eaten cooked (potatoes...) — non ready-to-eat FFVs. | | | | | | √ | 1 000 CFU/100 ml |
| ONLY POTABLE WATER
   (8) |
| Final washing and ice/water for cooling applied for ready-to-eat FFV | x | x | | | | √ | Microbiological requirements of potable water |

Intended use of the water

Source of water
   (1)

Indicator of faecal contamination: E. coli
   (2)

Untreated

surface water/open water channels (3)

Untreated ground water collected from wells (4)

Untreated

Rain water

Treated (5) sewage/surface/waste water/water reuse

Disinfected water (6)

Municipal water

PRE-HARVEST and HARVEST

Irrigation of FFVs likely to be eaten uncooked (i.e. ready-to-eat FFV) (irrigation water comes into direct contact with the edible portion of the FFV)

Dilution or application of pesticide, fertiliser or agrochemicals and cleaning equipment for ready-to-eat FFV and direct contact.

x

x

Image

Image

Image

√

100 CFU/100 ml

Irrigation of FFVs likely to be eaten uncooked (i.e. ready-to-eat FFV) (irrigation water does not come into direct contact with the edible portion of the FFV)

Dilution or application of pesticide, fertiliser or agrochemicals and cleaning equipment for ready-to-eat FFV and no direct contact

x

x

Image

Image

Image

√

1 000 CFU/100 ml (7)

Irrigation of FFVs likely to be eaten cooked (irrigation water comes into direct contact with the edible portion of the FFV).

Dilution or application of pesticide, fertiliser or agrochemicals and cleaning equipment used in this FFV direct contact).

Image

Image

Image

Image

Image

√

1 000 CFU/100 ml

Irrigation of FFVs likely to be eaten cooked (irrigation water does not come into direct contact with the edible portion of the FFV).

Dilution or application of pesticide, fertiliser or agrochemicals and cleaning equipment used in this FFV (no direct contact)

Image

Image

√

√

√

√

10 000 CFU/100 ml

POST-HARVEST

Post-harvest cooling and post-harvest transport for non-ready-to-eat FFVs.

Water used for first washing of products in case of ready-to-eat products.

Cleaning equipment and surfaces where the products are handled.

x

x

Image

Image

Image

√

100 CFU/100 ml

Water used for washing of products likely to be eaten cooked (potatoes...) — non ready-to-eat FFVs.

Image

Image

Image

Image

Image

√

1 000 CFU/100 ml

ONLY POTABLE WATER
   (8)

Final washing and ice/water for cooling applied for ready-to-eat FFV

x

x

Image

Image

Image

√

Microbiological requirements of potable water

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(1)  Water applied by irrigation within two weeks prior to harvest of FFVs that may be eaten uncooked (ready-to-eat) should be free of contamination, i.e. of potable quality wherever possible.

(2)  These recommended thresholds relate to maximum concentration in samples.

(3)  Surface water and Ground water from wells (e.g. boreholes) might be of good microbiological quality and meet the 100 CFU/100 ml thresholds without treatment.

(4)  Surface water and Ground water from wells (e.g. boreholes) might be of good microbiological quality and meet the 100 CFU/100 ml thresholds without treatment.

(5)  For the purpose of this matrix, treated sewage water means wastewater that has been treated so that its quality is fit for the intended use and complies with the standards established by the national legislation of the MS or, in the absence of such national legislation, with WHO guidelines on the safe use of wastewater and excreta in agriculture.

(6)  Disinfection treatment should be well controlled and monitored. The applied disinfection treatment is under the control of the grower or producer.

(7)  Since the irrigation water does not come into contact with the edible part of the FFV a value higher than 1 000 CFU/100 ml should be applied for E.coli. Irrigation methods such as drip or sub-surface will present a lower risk of contaminating the edible part of a lettuce FFV than overhead irrigation.

(8)  Multiple sources of water can be used but it must be potable water quality which needs to be delivered. So, in practice it will be municipal water or disinfected water which can be used here.

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ANNEX III

EXAMPLE OF A DECISION TREE TO SUPPORT MICROBIOLOGICAL RISK ASSESSMENT OF AGRICULTURAL WATER

This approach is simplified compared to the one described in Annex II, as the outcome takes into account a limited number of sampling recommendations. It is worth pointing out that results obtained from this decision tree (Annex III) and from the matrix (Annex II) cannot be comparable.

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Appendix

The Scope of Regulation (EC) No 852/2004 as regards food of non-animal origin

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