Guidelines for treatment and reuse of leachate from municipal solid waste (MSW) incineration plants

This document provides guidelines for the treatment and reuse of MSW leachate. It is applicable to personnel involved in the design, management, operation and supervision of the treatment and reuse of MSW leachate and environmental authorities engaged in regulation.

Lignes directrices pour le traitement et la réutilisation du lixiviat provenant des installations d'incinération des déchets ménagers

General Information

Status
Published
Publication Date
28-Jul-2022
Current Stage
6060 - International Standard published
Start Date
29-Jul-2022
Due Date
30-Jul-2022
Completion Date
29-Jul-2022
Ref Project
Standard
ISO 24297:2022 - Guidelines for treatment and reuse of leachate from municipal solid waste (MSW) incineration plants Released:29. 07. 2022
English language
29 pages
sale 15% off
Preview
sale 15% off
Preview

Standards Content (Sample)


INTERNATIONAL ISO
STANDARD 24297
First edition
2022-07
Guidelines for treatment and reuse of
leachate from municipal solid waste
(MSW) incineration plants
Lignes directrices pour le traitement et la réutilisation du lixiviat
provenant des installations d'incinération des déchets ménagers
Reference number
© ISO 2022
All rights reserved. Unless otherwise specified, or required in the context of its implementation, no part of this publication may
be reproduced or utilized otherwise in any form or by any means, electronic or mechanical, including photocopying, or posting on
the internet or an intranet, without prior written permission. Permission can be requested from either ISO at the address below
or ISO’s member body in the country of the requester.
ISO copyright office
CP 401 • Ch. de Blandonnet 8
CH-1214 Vernier, Geneva
Phone: +41 22 749 01 11
Email: copyright@iso.org
Website: www.iso.org
Published in Switzerland
ii
Contents Page
Foreword .iv
Introduction .v
1 Scope . 1
2 Normative references . 1
3 Terms and definitions . 1
4 Abbreviated terms . 2
5 General principles . 3
5.1 General . 3
5.2 Safety. 3
5.3 Reliability . 4
5.4 Stability . 4
5.5 Economic sustainability . 4
5.6 Environment . 4
6 Quantity and quality of the MSW leachate . 4
6.1 Quantity . 4
6.2 Quality . 5
6.3 Influencing factors and considerations . 6
7 Treatment system design for the MSW leachate . 6
7.1 Treatment process . 6
7.2 Treatment system . 7
7.2.1 Preliminary treatment . 7
7.2.2 Biological treatment . 8
7.2.3 Advanced treatment for reuse . 9
7.3 M onitoring system . 10
7.4 Auxiliary treatment . 11
7.4.1 General . 11
7.4.2 Sludge . 11
7.4.3 Concentrate . 11
7.4.4 Biogas .12
7.4.5 Odour .12
7.4.6 Foam . 12
7.4.7 Noise .12
8 Reuse of treated leachate .12
8.1 Reuse application considerations .12
8.2 Reclaimed water quality considerations .12
9 Environmental and occupational health and safety .13
9.1 Identification of health and safety risks . 13
9.2 Establishment of health and safety programmes . 13
9.3 Safety considerations in system design . 13
9.4 Implementation of health and safety equipment . 14
9.5 Training . 14
9.6 Management of incidents and emergencies . 14
Annex A (informative) Process parameters for leachate treatment system design .15
Annex B (informative) Quantity generation of MSW leachate .17
Annex C (informative) Potential treatment options for MSW leachate .18
Annex D (informative) Overview of MSW composition and treatment .19
Bibliography .28
iii
Foreword
ISO (the International Organization for Standardization) is a worldwide federation of national standards
bodies (ISO member bodies). The work of preparing International Standards is normally carried out
through ISO technical committees. Each member body interested in a subject for which a technical
committee has been established has the right to be represented on that committee. International
organizations, governmental and non-governmental, in liaison with ISO, also take part in the work.
ISO collaborates closely with the International Electrotechnical Commission (IEC) on all matters of
electrotechnical standardization.
The procedures used to develop this document and those intended for its further maintenance are
described in the ISO/IEC Directives, Part 1. In particular, the different approval criteria needed for the
different types of ISO documents should be noted. This document was drafted in accordance with the
editorial rules of the ISO/IEC Directives, Part 2 (see www.iso.org/directives).
Attention is drawn to the possibility that some of the elements of this document may be the subject of
patent rights. ISO shall not be held responsible for identifying any or all such patent rights. Details of
any patent rights identified during the development of the document will be in the Introduction and/or
on the ISO list of patent declarations received (see www.iso.org/patents).
Any trade name used in this document is information given for the convenience of users and does not
constitute an endorsement.
For an explanation of the voluntary nature of standards, the meaning of ISO specific terms and
expressions related to conformity assessment, as well as information about ISO's adherence to
the World Trade Organization (WTO) principles in the Technical Barriers to Trade (TBT), see
www.iso.org/iso/foreword.html.
This document was prepared by Technical Committee ISO/TC 282, Water reuse, Subcommittee SC 2,
Water reuse in urban areas.
Any feedback or questions on this document should be directed to the user’s national standards body. A
complete listing of these bodies can be found at www.iso.org/members.html.
iv
Introduction
Commonly used methods for disposal of municipal solid waste (MSW) include landfilling, incineration
and composting (Annex D), and each of these methods generates leachate. Leachate is a kind of
wastewater containing highly concentrated organic contaminants that can pose a high risk to the
environment. It is necessary for leachate to have proper treatment before being discharged or reused
to avoid adverse impacts on the environment. Due to the differences in duration of waste stacking and
fermenting, leachate from different MSW disposal methods varies significantly in the concentration and
biodegradability of organic matter, which requires tailored treatment processes. Leachate generated
from MSW incineration plants has a higher concentration of biodegradable organic pollutants, and
thus degrades more easily than leachate from landfills and composting plants. Due to higher quality
requirements for water reuse in MSW incineration plants, this document focuses on leachate treatment
and reuse in MSW incineration plants.
In MSW incineration plants the MSW first enters the unloading platform and then goes to the MSW
pit, where stacking and fermentation occurs. The stacking and fermenting process aims to reduce
moisture content of the MSW before incineration. The MSW leachate has a strong odour and high
concentrations of organic and inorganic compounds; it includes stacking and fermenting wastewater
and unloading platform flushing water. Many kinds of wastewater, such as municipal wastewater,
industrial wastewater and stormwater, are used as sources of reclaimed water to address worldwide
water shortages caused by economic growth, increasing populations, climate change and other factors.
The quality and quantity of MSW leachate can vary based on climate, residents’ living habits,
composition of waste and waste collection and separation systems. Therefore, leachate treatment can
be more challenging than other kinds of wastewater treatment. Due to the complex composition of
leachate and the high concentrations of pollutants, a combined treatment process is usually necessary
for leachate treatment to meet environmental requirements and intended reuse applications. The
essential components of the leachate treatment and reuse system include pretreatment, biological
treatment and advanced treatment.
In consideration of the problems in the treatment of MSW leachat
...

Questions, Comments and Discussion

Ask us and Technical Secretary will try to provide an answer. You can facilitate discussion about the standard in here.